University of Northampton - Northampton Borough Council
Transcription
University of Northampton - Northampton Borough Council
University of Northampton Document: GIH015-RPT-039 Version: 1 Northampton University Relocation Flood Risk Assessment September 2013 University of Northampton Northampton University Relocation Flood Risk Assessment September 2013 Halcrow Group Limited Red Hill House, 227 London Road, Worcester WR5 2JG tel 01905 361 361 fax 01905 361 362 halcrow.com Halcrow Group Limited is a CH2M HILL company Halcrow Group Limited has prepared this report in accordance with the instructions of the client, for the client’s sole and specific use. Any other persons who use any information contained herein do so at their own risk. © Halcrow Group Limited 2013 Document history This document has been issued and amended as follows: Version Date Description Created by Verified by Approved by 0 August 2013 Final Issue RB DPW DPW 1 September 2013 Revised as per comments received from Environment Agency on 16 September 2013 and response provided by Halcrow on 24 September 2013. RB BV DPW Contents 1 Introduction 1 1.1 1.2 1.3 Introduction Available Information Report Structure 1 1 1 2 Development Description and Location 3 2.1 Development Location and Description 3 3 Definition of Flood Hazard 4 3.1 3.2 3.3 3.4 Existing Drainage Characteristics Sources of Flooding and Existing Flood Defences Surface Water Drainage and overland flow routes Other sources of Flooding 4 6 7 7 4 Probability of Flooding 8 4.1 4.2 4.3 4.4 4.5 4.6 Environment Agency modelled River Nene flood extents and levels Speed with which fluvial flooding might occure SFRA Level 1 (February 2009) SFRA Level 2 (February 2010) Upton Flood Attenuation Area Surface Water Flooding 5 Climate Change 15 6 The Development Proposals 16 6.1 6.2 6.3 6.4 Waterside Campus Site Layout Drainage Strategy Overland Flow Routes Adoption and Maintenance of the surface water drainage and SuDS 7 Flood Risk Management 7.1 7.2 7.3 7.4 7.5 7.6 Fluvial Flooding Structures which may influence local hydraulics Surface water flooding Other sources of flooding Maintenance of sustainable drainage systems Maintenance Access for River Nene and Hardingstone Dyke 8 10 10 12 14 14 16 17 17 17 18 18 19 20 20 20 21 8 Off Site Impacts 8.1 8.2 8.3 8.4 Fluvial flooding Breach of Northampton flood defences Surface water flooding Fluvial Morphology 9 Residual Risks 9.1 9.2 9.3 Breach of Northampton Flood Defences Surface water drainage exceedance flows Flood warning and evacuation 10 EA Strategic Review and Update 27 10.1 Compliance with EA Strategic Review and Update 27 11 Conclusions 31 12 References 33 22 22 24 24 24 25 25 26 26 Appendices Appendix A NPPF Sequential Test for the proposed Relocation of the University of Northampton Appendix B – SFRA Level 2 Figures D-6 and D-7 Appendix C – Technical Note: University of Northampton Relocation breach analysis modelling Appendix D – Data received from the Environment Agency Appendix E – Site cross sections pre and post development and details of proposed road, River Nene Road Bridge and foot/cycle bridge Appendix F – Outline Foul, Surface Water Drainage and SuDS Strategy and associated calculations Figures 1 Introduction 1.1 Introduction This flood risk assessment supports the University of Northampton Relocation to Waterside Campus planning application, which proposes development of the Waterside Campus site (also known as the Avon and Nunn Mills Roads development sites) as a University Campus. 1.2 Available Information Key information considered when preparing this flood risk assessment includes: • • • • • • • • • • 1.3 National Planning policy Framework (NPPF) and Technical Guidance to the NPPF PPS25 (now superseded by NPPF – but NPPF retains much of PPS25) Current Environment Agency modelled River Nene flood levels and flood extents West Northamptonshire SFRA Level 1 (Feb 2009) Northampton SFRA Level 2 (Feb 2010) Northampton Waterside Campus development design Environment Agency breach analysis results for Northampton and further breach analysis undertaken by University of Northampton for the University Relocation to Waterside Campus planning application. Hydraulic modelling and results undertaken by the Homes and Communities Agency for the Ransome Road development site planning application Hydraulic modelling and results undertaken by the West Northamptonshire Development Corporation for the Nunn Mills Road upgrade/extension planning application Other references are included in Section 12. Report Structure As the NPPF retains key aspects of PPS25, for ease of reference to PPS25 requirements, Sections 2 to 9 of this report are structured according to the Flood Risk Assessment Checklist provided in the PPS25 Practice Guide. Compliance with the Environment Agency’s Strategic Review of Development and Flood Risk: Nene Catchment Northampton and Upstream and its update is in Section 10. Conclusions are in Section 11 and references are listed in Section 12. Appendix A demonstrates that the proposed University of Northampton Relocation to Waterside Campus development passes the NPPF Sequential Test. The SFRA Level 2 Figures D-6 and D-7, including breach analysis results relevant to the University of Northampton Relocation site, are reproduced in Appendix B. A technical note detailing breach analysis undertaken for the University of Northampton Relocation proposed Waterside Campus site is in Appendix C. Appendix D includes information received from the Environment Agency to support this flood risk assessment. Appendix E contains plan and long section drawings of the proposed new access road and River Nene bridge and details of the proposed culvert and typical proposed road cross sections. Information relating to the proposed sustainable drainage systems is in Appendix F: Outline Foul, Surface Water Drainage and SuDS Strategy and associated calculations. 2 Development Description and Location 2.1 Development Location and Description The location of the proposed Waterside Campus development is shown in Figure 1. The proposed development is located approximately 1 km to the east of Northampton town centre. The planning application boundary includes: • • • • • the Avon/Nunn Mills development site south of the River Nene the existing Nunn Mills Road and its junction with Bedford Road land to the east of the existing Nunn Mills Road River Nene crossing to allow for a new River Nene crossing land to allow for a new foot/cycle bridge connecting the north-west corner of the Avon/Nunn Mills development site to Northampton land to allow for an electricity substation in the south-east corner of the application site The application boundary crosses the River Nene and Nene navigation and borders Hardingstone Dyke. The proposed development layout is shown in Figure 2. The development includes: • • • • • • • • • • • • Academic facilities Student accommodation Social and sports/leisure buildings Sports pitches Car parking Commercial office buildings Hotel Energy centre Access roads, footpaths and cycle-ways New river Nene road/foot/cycle bridge New River Nene footbridge/cycle bridge No works are proposed on Delapre Brook Whilst the proposed new road will not, as part of the University development proposal, extend southwards into the Ransome Road development, the masterplan enables a future “Green Link” facilitating Bus, Pedestrian and Cycle Movement with minimal levels of through traffic to enable delivery of strategic development in the Waterside: Avon/Nunn Mills/Ransome Road area of Northampton, identified in the Northampton Central Area Action Plan January 2013. The NPPF vulnerability classification of the proposed development is considered as follows: • • • Essential infrastructure - proposed road upgrade and extension (the proposed road is required for the planned strategic development in the Waterside area) - energy centre Less vulnerable - academic facilities - social and sports/leisure buildings - sports pitches - car parking - commercial office buildings - access roads, paths and cycle-ways More vulnerable - student accommodation - hotel A NPPF Sequential Test for the proposed University of Northampton Waterside Campus development is included in Appendix A. 3 Definition of Flood Hazard 3.1 Existing Drainage Characteristics The Waterside Campus development site location is described in Section 2.1. The principal hydrological features in the vicinity of the proposed development are: • • • • • River Nene Hardingstone Dyke Delapre Brook Delapre Lake Drainage ditch along the southern edge of the railway line to the south of Hardingstone Dyke The Kislingbury and Brampton branches of the River Nene converge about 250m upstream of South Bridge where the combined flow in the river is gauged. South Bridge is a key gauging station and the flood levels here are often used as an indicator of the flooding situation in Northampton. Downstream of South Bridge, the flow in the River Nene is controlled by a set of hydraulic structures at the southern end of Beckett’s Park. Water levels in the main river channel are controlled by Nunn Mills Sluice which is situated immediately upstream of the Nunn Mills Road bridge. The sluice consists of three parallel vertical steel lifting gates. Upstream of the Nunn Mill Sluice, there are three bypass channels on the left bank of the Nene which convey water from the higher level main channel to a lower level channel. Immediately upstream of the Nunn Mills Sluice, the first bypass channel is controlled by Red House Sluice which is a modern structure with a single tilting gate. Upstream of that, the second bypass channel is controlled by Calvesholme Weir which is an old iron tilting-gate weir. The third channel is the navigation channel which consists of Northampton Town Lock. The three bypass channels join up on the northern side of Beckett’s Park upstream of Nunn Mills Road and converge with the main channel a further 100m downstream of Nunn Mills Sluice. A further 1500m downstream, the next control structure on the Nene is the Rush Mills Sluice. Hardingstone Dyke is a catchwater drain which runs parallel to the Nene on its southern side. It intercepts flow from minor tributaries along the southern side of the valley between Cotton End and Little Houghton where it discharges into the river. Hardingstone Dyke is classified as a Main River and splits into two branches. The first branch continues in a straight line as far west as Old South Bridge Road. The second branch, which is connected to the first branch by a culvert just east of Nunn Mills Road crossing runs along the northern side of the railway line. At its upstream end at Cotton End Road, it is fed by a pair of surface water sewers. Delapre Brook, which is also sometimes referred to as Ransome Road Drain or Hardingstone Drain, is classified as Main River and runs for a distance of 900m along the northern boundary of Delapre Park from London Road (A508) to Delapre Lake into which it discharges. Delapre Lake drains into Hardingstone Dyke upstream of the A45 road crossing, via a concrete weir into an open channel followed by approximately 25m of 750mm diameter pipe. Delapre Brook is classified as main river including through Delapre Lake, which is approximately 750m long and would provide significant attenuation of Delapre Brook flood flows. There is a railway drainage ditch south of the railway line adjacent to Hardingstone Dyke, draining west-east. This collects local surface water drainage only and eventually drains to Hardingstone Dyke, north of Delapre Lake. The Ransome Road development proposals (Homes and Communities Agency, 2010) include extending the railway ditch westwards to collect surface water runoff from the developed site (Appendix C). A minor drain receiving local surface water drainage is culverted under the Nunn Mills Road alignment, approximately 20m north of the Hardingstone Dyke crossing, and this becomes open channel east of Nunn Mills Road. 3.2 Sources of Flooding and Existing Flood Defences The principal source of flooding for the Waterside Campus development site is from the River Nene. Flood defences in the vicinity of the Waterside Campus site are mapped and described in Appendix D. South of the River Nene, the Northampton Flood Alleviation Scheme includes an earthen embankment along part of the Avon Cosmetics site riverbank, designed to provide a 1 in 200 year level of protection. Flood defences upstream of the site have also been improved and the flow paths of the 1998 flood, during which the River Nene burst its banks upstream of South Bridge and water came over Cotton End Road, have now been blocked (Northampton flood defences were designed to provide a 200-year standard of protection and are reported in NFCDD to be in good condition). More extreme events would result in overtopping of the defences and would affect the site. North of the River Nene, flood defences directly downstream of Nunn Mills Road comprise of a flood bank designed to a 200 year standard of protection. Upstream of Nunn Mills Road, land to the north of the river in Beckett’s Park rises away from the river and the extent of any flooding in Beckett’s Park is limited by the topography. The impact on the Waterside Campus site of breaching of Northampton flood defences is considered in Section 9.1. Two sewers draining part of Cotton End discharge into Hardingstone Dyke at the west end of Thomas Chapman Grove. There is no history of flooding in the development site from Hardingstone Dyke and its capacity is significantly more than the sewer that discharges into it. Hardingstone Dyke discharges into the River Nene at Clifford Hill, more than 4 km downstream of Nunn Mills Road and flood-locking of the Dyke can be disregarded. Two large sewers of 750mm and 600mm diameter draining Far Cotton discharge into Delapre Brook which in turn discharges into Delapre Lake and onwards to Hardingstone Dyke. Anecdotal evidence suggests that due to fly tipping and obstructions of culverts in the drain, localised flooding occasionally occurs on the right bank in Delapre Park. However, this is not regarded as a serious issue if obstructions from the drain are cleared. The development site is not affected as adjacent land north of Delapre Brook is at elevated levels. As Delapre Brook is a tributary of Hardingstone Dyke, but separated from it by Delapre Lake, flood-locking of the drain may be disregarded. The railway ditch, south of the railway adjacent to Hardingstone Dyke and draining west-east, collects local surface water drainage only and so is not considered a significant source of flooding. 3.3 Surface Water Drainage and overland flow routes The existing surface water drainage for the application site is described in Section 5.1 of the Outline Foul, Surface Water Drainage and SuDS Strategy in Appendix F. Existing overland flow routes are shown in Figure 3. 3.4 Other sources of Flooding The site is not considered to be at risk of groundwater flooding or tidal flooding. 4 Probability of Flooding 4.1 Environment Agency modelled River Nene flood extents and levels 4.1.1 Flood extents Figure 4 shows historic flood outlines for the 1947 and 1998 and floods. The proposed Waterside Campus site is shown to be within the 1947 flood extent and partly with the 1998 flood extents. The 1998 event was thought to have a return period between 75 and 150 years and was the most severe event in recent memory. However, since the 1998 event, flood defences have been constructed in Northampton designed with a 200-year standard of protection. The current Environment Agency Flood Zones 2 and 3 are shown in Figure 5 as the Area at risk of Flooding from Rivers or the Sea and Extreme Flood Outline respectively. These correspond directly to the NPPF Zones which do not account for flood defences. Figure 5 also shows Areas Benefitting from Defences. The Environment Agency modelled flood extents are shown in Map 5 in Appendix D. The modelling allows for flood defences and overtopping of the defences where modelled river levels are higher than the defence levels. The modelling includes the recently constructed Upton Flood Attenuation Area. The proposed Waterside Campus site is shown in Figure 5 to be mostly in the Environment Agency Flood Zone 3 with some areas in Zones 2 and 1 (Zone 1 is the area outside Zones 2 and 3). However, the Environment Agency Flood Zones do not allow for flood defences and Map 5 in Appendix D shows the proposed development to be outside the modelled 100-year flood extent (accounting for flood defences) except for the River Nene corridor and parts of the Beckett’s Park river island. 4.1.2 Environment Agency breach modelling results The Environment Agency breach modelling results included in Appendix D show the Waterside Campus development site to be at risk of a breach of Northampton flood defences. The figures show significant flooding on the Waterside Campus development site following a breach of Northampton flood defences during the 200-year return period flood with climate change allowance, including areas with Defra flood hazard classification Danger for Most both upstream and downstream of Nunn Mills Road. The proposed Waterside Campus development removes this residual flood risk through land raising with mitigation provided by Upton Flood Attenuation area (Section 7.1). Breach modelling has been undertaken to assess residual flood risk for the proposed Waterside Campus development, reported in Section 9 and Appendix C. 4.1.3 Modelled flood levels For this flood risk assessment hydraulic modelling has been undertaken to assess the impact of the proposed development on flood risk including the consequences of a breach of Northampton flood defences. The modelling for this was developed from the current version of the Environment Agency’s Upper Nene Catchment Strategic Model (2013). The Environment Agency Upper Nene model represents the current situation, including the Upton Flood Attenuation Area upstream of Northampton. Environment Agency modelled flood levels (taken from data provided for this FRA – see Appendix 4.1.2) in the vicinity of the proposed Waterside Campus site are listed in Table 2. Location in River Model Node Modelled Flood Levels (mAOD) 200-year with climate change allowance 1000-year with climate change allowance Upstream end of Waterside Campus site a7455 58.72 59.05 Approx. 100m upstream of Nunn Mills sluice gates a7436a 58.37 58.68 Approx. 50m upstream of Nunn Mills sluice gates a7414a 58.12 58.47 Location of proposed new River Nene bridge a7403 57.86 58.20 Downstream end of Waterside Campus site a7365 57.69 57.99 Hardingstone Dyke at upstream end of Waterside Campus site sec003 56.91 58.67 Hardingstone Dyke at upstream end of Nunn Mills Road culvert sec07u 56.51 58.39 Hardingstone Dyke at downstream end of Waterside Campus site sec019 56.28 57.83 Table 2: Modelled flood levels in the River Nene and Hardingstone Dyke near the Waterside Campus site 4.2 Speed with which fluvial flooding might occur The proposed Waterside Campus development is located behind existing flood defences (or above River Nene flood levels at the bridge crossings). Northampton flood defences were designed to provide a standard of protection of 200 years. It is highly unlikely that this rare event would not be preceded by a considerable lead in time to provide adequate flood warning. In the Upper Nene Catchment, the time to peak at Southbridge, upstream of the proposed Northampton University Relocation site, is approximately 36 hours in the Brampton Nene and 32 hours in the Kislingbury Nene. This is based on the Environment Agency simulated 200-year with climate change allowance design flood in Northampton. The impacts of a breach of Northampton defences on the proposed Waterside Campus development have been investigated by hydraulic modelling. This modelling is reported in Appendix C. For the modelled breach scenarios, breach flood water does not reach the Waterside Campus site. 4.3 SFRA Level 1 (February 2009) The West Northamptonshire SFRA Level 1 was completed in February 2009. When assessing flood risk at planned development sites in Northampton, the West Northamptonshire SFRA Level 1 summarises the assessment made in the Northampton Borough Council SFRA (2004). This acknowledges the effect of flood defences by classifying the part of the Waterside Campus proposed development site in the defended floodplain as PPG25 Zone 2 (equivalent to NPPF Zone 2) rather than Zone 3. However the Environment Agency Flood Zones are defined ignoring the presence of defences and the defended floodplain is classified as Flood Zone 3. The proposed University of Northampton Waterside Campus (i.e. all of the proposed University of Northampton development excluding the new road/road bridge, the foot/cycle bridge and the energy centre) is classified as less vulnerable and more vulnerable development (Section 2.1) and is shown in Figure 5 to be all within Flood Zone 3a (defended River Nene floodplain). NPPF considers less vulnerable development to be appropriate in Flood Zone 3a. For the more vulnerable development (comprising student accommodation and hotel) the NPPF Exception Test is required to be passed. Table 3 details how the proposed Waterside Campus development passes the Exception Test. Where the proposed new road crosses the River Nene the development site is in Flood Zone 3b. NPPF considers the essential infrastructure and water compatible development classes to be appropriate in Flood Zone 3b and essential infrastructure in this zone should pass the Exception Test. The proposed new road is considered essential transport infrastructure, providing access/egress for development planned in the Waterside area (including the proposed University of Northampton Waterside Campus development and the Ransome Road development site. Table 3 details how the proposed new road essential infrastructure passes the Exception Test. Appendix A demonstrates that the proposed Waterside Campus site passes the NPPF Sequential Test. NPPF Exception Test Requirement How Passed It must be demonstrated that the development provides wider sustainability benefits to the community that outweigh flood risk, informed by a Strategic Flood Risk Assessment where one has been prepared. The proposed relocation of University of Northampton to Waterside Campus contributes to the regeneration of urban Northampton. The proposed new road as part of the University development proposal, extends southwards towards the Ransome Road development and the masterplan enables a future “Green Link” facilitating Bus, Pedestrian and Cycle Movement with minimal levels of through traffic to Ransome Road The Waterside Campus brownfield site is identified as a strategic development site in the Northampton Level 2 SFRA (i.e. the Nunn Mills site) and the proposed use of the site for relocation of University of Northampton is considered appropriate in the Northampton Central Area Action Plan. A site-specific flood risk assessment must demonstrate that the development will be safe for its lifetime taking account of the vulnerability of its users, without increasing flood risk elsewhere, and, where possible, will reduce flood risk overall. This FRA report demonstrates that the development will be safe without increasing flood risk elsewhere. Upton Flood Attenuation Area (FAA) provides strategic mitigation for development planned in and around Northampton, including the proposed Waterside Campus development. Upton FAA reduces flood risk throughout Northampton over a significantly wider area than the proposed Waterside Campus site. Table 3: NPPF Exception Test for proposed Waterside Campus development 4.4 SFRA Level 2 (February 2010) The Northampton SFRA Level 2 was completed in February 2010. This assesses residual flood risk behind Northampton flood defences and includes the impacts of modelled breaches on Northampton during a 200year return period flood. The potential breaches considered to have most impact on flood risk at the proposed Waterside Campus site (in terms of highest depths, velocities and hazard scores) are a breach of the Carlsberg sluice, approximately 80m upstream of Southbridge (SFRA Level 2 Breach 5) and a breach of flood defence embankments south of the River Nene upstream of Nunn Mills Road (SFRA Level 2 Breach 6). The SFRA Level 2 breach modelling considers breaching of Northampton flood defences during the 200-year return period flood only (without an allowance for climate change). However, the NPPF requires the impacts of climate change on flood risk to be considered. Figures D-6 and D-7 of the SFRA Level 2 are reproduced in Appendix B. The SFRA Level 2 results show no flooding on the Nunn Mills Road site as a result of Breach 5. For Breach 6, there is modelled flooding on the Waterside Campus site upstream of the existing Nunn Mills Road. The Environment Agency has undertaken breach modelling for Northampton including modelling the consequences of a breach during the 200-year return period with climate change allowance flood. These results inform this FRA and are developed further to consider the impacts of the proposed Waterside Campus development on the consequences of a breach of Northampton defences (Section 9.1 and Appendix C). The proposed University of Northampton Relocation development includes raising ground levels such that a breach of Northampton flood defences along the northern edge of the site is no longer considered a significant risk, since the proposed levels adjacent to the flood defences are above the 1000-year with climate change allowance modelled flood level (and the raised levels extend into the site rather than form raised embankments). Table 4 includes the policies and recommendations for the Nunn Mills Road site (which corresponds to the proposed Waterside Campus site) presented in Table 5-2 of the SFRA Level 2 and how these are addressed in this Flood Risk Assessment. Area (as defined in SFRA Level 2) SFRA Level 2 Table 5-2 policies and recommendations How addressed in this FRA Nunn Mills Road The area affected by a breach in embankment at location 6 is limited to the north of the area, to the west of Nunn Mills The proposed University of Northampton Relocation development includes raising ground levels such that a breach of Northampton flood defences along the northern edge of the site (including the SFRA Breach 6) is no longer considered a significant risk, since the proposed levels adjacent to the flood defences are above the 1000-year with climate change allowance modelled flood level (and the raised levels extend into the site rather than form raised embankments). The breach modelling undertaken for this study assesses a breach directly upstream of South Bridge, at Carlsberg Sluice, during a 200-year return period with climate change allowance flood in the River Nene. Road and flooding is not extensive. Generally a breach would present ‘Danger for Some’, with some pockets of deeper, faster flowing water presenting ‘Danger for Most’. The proposed Waterside Campus development is designed to be safe from flooding during a breach of Northampton flood defences and the new road will provide safe access/ egress routes following a breach of Northampton defences (Section 7.2, Section 9 and Appendix D). Any future proposed development should be rolled back from the watercourse. More vulnerable and highly vulnerable development should be located to the south of the area, with less vulnerable and water compatible development being more appropriate towards the north of the area. Due to the orientation of the site in relation to the River Nene, a breach could occur at any point along the defences. This is important to note at site-specific FRA stage as only a single breach has been considered as part of the Level 2 SFRA. The proposed Waterside Campus development is considered Essential Infrastructure, Less Vulnerable and More Vulnerable. Following the proposed land raising on the Waterside Campus site the risk of a breach of the River Nene flood defences along the northern edge of the proposed campus is removed. Following the proposed land raising as part of the Waterside Campus development, the most likely location for a breach that could impact the Waterside Campus site is considered to be at Carlsberg sluice, upstream of Southbridge. A breach at this location has been modelled, with a breach commencing at the peak river level during the design 200-year with climate change allowance flood. Table 4: SFRA Level 2 policies and recommendations for the Waterside Campus development site 4.5 Upton Flood Attenuation Area Upton Flood Attenuation Area, upstream of Northampton, was implemented by the Homes and Communities Agency as strategic infrastructure to mitigate increased flood risk due to planned development in and around Northampton, including the development of the proposed Waterside Campus site. 4.6 Surface Water Flooding Existing rates and volumes of runoff generated by the site, used in designing the proposed drainage scheme, are included in Appendix F. 5 Climate Change The NPPF requires the assessment of flood risk to account for the impacts of predicted climate change. To account for predicted climate change, following current NPPF guidance, an additional 20% has been added to modelled fluvial inflows in the hydraulic modelling used within this assessment. The drainage design for the proposed development will be carried out with an allowance for climate change in accordance with Table 5 of the “Technical Guidance to the National Planning Policy Framework” March 2012. The climate change allowance is dependent upon its design life and for a university development, a design life up to 2085 is appropriate with an associated 20% increase to peak rainfall intensity for determining attenuation requirements. A residential development would normally attract a design life of up to 2115 and a 30% climate change allowance, however it is considered that as the 1500 residential units are for university accommodation, are integral to the university development and dependant on it, it is appropriate to consider them as part of the university in terms of design life with the associated 20% climate change allowance. 6 The Development Proposals 6.1 Waterside Campus Site Layout The proposed Waterside Campus development site layout is shown in Figure 2. The proposed scheme includes: • • • • • • • • • • • • Academic facilities Student accommodation Social and sports/leisure buildings Sports pitches Car parking Commercial office buildings Hotel Energy centre Access roads, footpaths and cycle-ways New river Nene road/foot/cycle bridge New River Nene footbridge/cycle bridge No works are proposed on Delapre Brook The proposed development is considered to include the NPPF vulnerability classifications essential infrastructure, less vulnerable and more vulnerable (Section 2.1). The development site is mostly within Flood Zone 3a with some Flood Zone 1, 2 and 3b. Section 4.3 considers the Waterside Campus site flood zones and appropriate development. A NPPF Sequential Test for the proposed University of Northampton Waterside Campus development is included in Appendix A. Cross sections showing the Waterside Campus pre- and post-development are in Appendix E. These show that for the proposed Waterside Campus ground levels are raised above the 200-year with climate change flood level with a breach of Northampton flood defences. Ground levels are not raised in the vicinity of the existing engine shed, which is a listed building, however the engine shed is outside of the 200-year with climate change flood level with a breach of Northampton flood defences. A plan and long section of the proposed new road and new River Nene bridge are in Appendix E. The proposed new road and River Nene road crossing is designed to provide safe access/egress during the 1000-year with climate change allowance River Nene flood, whilst not increasing flood risk elsewhere for a breach of Northampton flood defences during the 200-year with climate change allowance flood in the River Nene. The soffit level of the new bridge is design to provide 3m clearance above the normal water level for navigation and so the soffit is significantly higher than the 1000-year with climate change allowance modelled flood level. The design for proposed foot/cycle bridge has not yet been finalised but it will be a clear span with soffit levels above the 1000-year return period with climate change allowance flood level (at least 3m above normal water level to meet navigation requirements) and designed to have no negative impact on flood risk compared to the base case model (i.e. Upton Flood Attenuation Area provides mitigation). The outline design of the proposed foot/cycle bridge is shown in appendix E. The proposed Ransome Road development FRA (Homes and Communities Agency, 2010) includes extending the existing drainage ditch running west-east along the southern side of the railway crossed by the proposed Nunn Mills Road. The Ransome Road FRA specified a 10m wide channel width for this ditch to convey breach flood flows, and this channel width is therefore retained in the modelled representation of the proposed Ransome Road development during this proposed Waterside Campus development flood risk assessment. 6.2 Drainage Strategy The Surface Water Drainage and SuDS Strategy for the proposed development are detailed in Section 5 of Appendix F: Outline Foul, Surface Water Drainage and SuDS Strategy. 6.3 Overland Flow Routes For storms exceeding the drainage system capacity surplus runoff will be routed overland as shown in Figure 6. In line with the design criteria set out in Section 5.2 of Appendix F, exceedance flows will not flood proposed and retained buildings for storm events with a return period bigger than in 200 years plus 20% climate change. In accordance with best practice (CIRIA C635 Designing for Exceedance), flood water from the storm events that exceed the design storm of 1 in 200 years plus 20% climate change will be channelled towards the lower areas like the car parks, the pond and then discharge into Hardingstone Dyke or River Nene. Further details are in Appendix F. 6.4 Adoption and Maintenance of the surface water drainage and SuDS The proposed adoption and maintenance arrangements for the development surface water drainage and Sustainable Drainage Systems (SuDS) are in Section 7 of Appendix F: Outline Foul, Surface Water Drainage and SuDS Strategy. The drainage system within the Avon site (excluding Avon Building) will be private and will have to be maintained by a private management company. However, the proposed surface water drainage system and SuDS within Nunn Mills site can be offered for adoption to Anglian Water under the Section 104 Agreement of the Water Industry Act based on the assumption that commercial buildings will be owned by different parties/people. If piped networks are to be offered for adoption to Anglian Water, these will be subject to Easement Agreements along the proposed sewers. If SuDS are offered for adoption this process will involve land ownership transfer from future land owner to Anglian Water. The extent of this will have to be determined through liaisons with Anglian Water. The drainage in the adopted highway will be maintained by the Local Highway Authority as part of its routine maintenance programme to ensure operation of the system. 7 Flood Risk Management 7.1 Fluvial Flooding The Waterside Campus development site is mostly in the River Nene defended floodplain, protected from flooding by Northampton flood defences. The defences were designed with a 200-year designed standard of protection. The proposed Waterside Campus development will not compromise the effectiveness of the existing flood defences. Those parts of the development within the active floodplain are the proposed new River Nene bridge and part of the new road within the River Nene Flood Zone 3b and the part of the proposed new foot/cycle bridge within Flood Zone 3b. Construction of Upton Flood Attenuation Area (FAA) upstream of Northampton was completed in 2009. Upton FAA was implemented by the Homes and Communities Agency ahead of development in and around Northampton to mitigate any associated increase in flood risk. Upton FAA is designed to reduce flood levels in the River Nene in Northampton with a modelled reduction in peak flood level at Southbridge, for the 200-year with climate change allowance flood, by approximately 350mm (source: Upton FAA Flood Risk Assessment). The proposed new road is designed to provide a safe access route for planned development in the area during the modelled 1000-year with climate change River Nene flood. Modelled post-development peak flood depths, velocities and hazard scores within the 2D hydraulic model domain, during the 1000-year return period with climate change allowance River Nene flood, are shown in Figures C5 and C6 (Appendix C) for the cases without and with development of the Ransome Road site respectively. Figures C7 and C8 show that the proposed new road provides a safe route within the 2D hydraulic model domain for the cases without and with development of the Ransome Road site, i.e. the maximum hazard score along the proposed new access road is ‘very low’ as classified in Defra project report FD2320. The new River Nene bridge is represented in the 1D model domain. Table 5 list modelled peak 1000-year return period with climate change allowance flood levels in the River Nene in the vicinity of the new River Nene bridge for the cases that Nunn Mills Road is constructed both with and without the planned Ransome Road development. For the proposed new road lying within the 1D hydraulic model domain, the design road levels are a minimum of 60.6 mAOD and significantly higher than the modelled 1000-year with climate change allowance peak flood levels in Table 5. To meet River Nene navigation requirements, the soffit level of the proposed new foot/cycle bridge will be a minimum of 3m above the normal River Nene water of 57.2mAOD level (i.e. a minimum of 60.2mAOD). This is significantly higher than the modelled 1000-year with climate change allowance peak flood levels at the foot/cycle bridge location in Table 5. The proposed development includes land raising within the University of Northampton Waterside Campus to remove the risk associated with a breach of Northampton flood defences. The extent of land raising and site cross sections are shown in Appendix E. The proposed land raising increases ground levels adjacent to the River Nene flood defences to be above the 1000-year return period with climate change modelled flood levels. There is no land raising adjacent to the existing engine shed as it is a listed building. However, post-development, the whole of the proposed University of Northampton Waterside Campus will be outside of the modelled 200year return period with climate change allowance flood extent (Figures C2 and C3 in Appendix C). Finished floor levels will be a minimum of 300mm above the modelled 200-year return period with climate change allowance flood level (including with a breach of Northampton flood defences). Flood risk due to breaching of Northampton flood defences is discussed as a residual risk in Section 9.1 and Appendix C. Modelled post-development 1000-year with climate change allowance peak flood level (mAOD) Without development of the Ransome Road site With development of the Ransome Road site Location of new foot/cycle bridge (model node a7445) 57.90 57.89 Upstream of new River Nene bridge (model node a7403) 58.62 58.62 Downstream of new River Nene bridge (model node a7403i2) 57.89 57.88 Location Table 5: Modelled peak 1000-year return period with climate change allowance flood levels in the River Nene 7.2 Structures which may influence local hydraulics There are no structures planned for the proposed development which will adversely influence local hydraulics. The proposed new River Nene bridge will span the River Nene with no piers and have a soffit level above the 1000-year return period with climate change allowance flood level (Section 7.1). Hydraulic modelling indicates the new bridge has a marginal impact directly upstream where there is a slight and localised increase in modelled floodplain depths (modelled depth increase between 0mm and 20mm) directly upstream of the proposed new bridge. This is considered an insignificant impact as the level increase is marginal and only affects the floodplain adjacent to a car park which remains dry during the modelled 1000-year with climate change allowance flood for the post-development case (Figures C5 and C6 in Appendix C), and the Waterside Campus development site, for which there will be land raising above the 1000-year with climate change flood level adjacent to the River Nene. Upton Flood attenuation area provides mitigation for the new road and bridge. The proposed foot/cycle bridge is at a preliminary design stage. The bridge will have a soffit level above the modelled 1000-year return period with climate change allowance flood level and will be designed to have no adverse impact on flood risk elsewhere. The proposed development will include improvement works where possible to the Hardingstone Dyke, which will be developed in detail with the Environment Agency as part of the Reserved Matters applications as the detailed design develops. Whilst the proposed new road does not continue as far south as the Hardingstone Dyke crossing, the new road has been designed so that it can be extended to provide access to the Ransome Road development site. The hydraulic modelling for this flood risk assessment assumes that when extended, the Ransome Road site access road will include a 2.7m wide Hardingstone Dyke culvert, and the two channels south of Hardingstone Dyke will be crossed with 10m wide culverts (these are required to convey breach flood flows). The proposed Ransome Road development FRA (Homes and Communities Agency, 2010) includes extending the existing drainage ditch running west-east along the southern side of the railway. The Ransome Road FRA specified a 10m wide channel width for this ditch to convey breach flood flows, and this channel width is therefore retained in the representation of the Ransome Road development in this flood risk assessment. The Ransome Road development will need its own FRA and ground re-modelling, but the FRA for the Waterside development does not place any more onerous requirements on this site. 7.3 Surface water flooding Current and proposed surface water drainage arrangements are described in Appendix F. The proposed surface water drainage strategy limits outflows from the proposed development to pre-development rates for storms up to a 200-year return period with allowance for climate change. For larger storms surplus runoff will be routed over land as shown in Figure 6. 7.4 Other sources of flooding The site is located upstream of the limit of tidal influence on the River Nene and there is no risk of tidal flooding. The site is not considered to be at risk of groundwater flooding. 7.5 Maintenance of sustainable drainage systems The proposed adoption and maintenance arrangements for the development surface water drainage and Sustainable Drainage Systems (SuDS) are in Section 7 of Appendix F: Outline Foul, Surface Water Drainage and SuDS Strategy. The drainage system within the Avon site (excluding Avon Building) will be private and will have to be maintained by a private management company. However, the proposed surface water drainage system and SuDS within Nunn Mills site can be offered for adoption to Anglian Water under the Section 104 Agreement of the Water Industry Act based on the assumption that commercial buildings will be owned by different parties/people. If piped networks are to be offered for adoption to Anglian Water, these will be subject to Easement Agreements along the proposed sewers. If SuDS are offered for this process will involve land ownership transfer from future land owner to Anglian Water. The extent of this will have to be determined through liaisons with Anglian Water. The drainage in the adopted highway will be maintained by the Local Highway Authority as part of its routine maintenance programme to ensure operation of the system. 7.6 Maintenance Access for River Nene and Hardingstone Dyke The River Nene and Hardingstone Dyke are classified as Main River and so are maintained by the Environment Agency. The proposed Waterside Campus development therefore allows a minimum of 5m access strips to maintain the River Nene and Hardingstone Dyke. 8 Off Site Impacts 8.1 Fluvial flooding The proposed Waterside Campus development is mostly in the River Nene defended floodplain, protected from flooding by Northampton flood defences. The defences were designed to provide a 200-year standard of protection. Those parts of the development within the active floodplain are the proposed new River Nene road bridge and the proposed foot/cycle bridge. The proposed new River Nene bridge is designed to have negligible impact on flood flows and levels. Construction of Upton Flood Attenuation Area (FAA) upstream of Northampton was completed in 2009. Upton FAA was implemented by the Homes and Communities Agency ahead of development in and around Northampton to mitigate any associated increase in flood risk. This includes mitigation of increased flood risk associated with the Waterside Campus development. When assessing the impact of the proposed Waterside Campus on flood risk the pre-development case is therefore taken to be pre-development of Waterside Campus and pre-construction of Upton FAA. The post-development case is assessed for the cases with and without the planned Ransome Road development as the Waterside Campus development may take place before or after the planned Ransome Road development. Upton FAA is designed to reduce flood levels in the River Nene in Northampton with a modelled reduction in peak flood level at Southbridge, for the 200-year with climate change allowance flood, by approximately 350mm (source: Upton FAA Flood Risk Assessment). Elements of the proposed Waterside design requiring mitigation are: • • • Displaced defended floodplain potential storage due to land raising within the Waterside Campus area Displaced active and defended floodplain storage due to construction of the proposed new road connecting the Waterside Campus development to Bedford Road Displaced defended floodplain potential storage due to construction of the proposed new foot/cycle bridge The impacts of the proposed development are assessed by comparing predevelopment and post-development; • • flood levels in the River Nene 1D model extent and; gridded flood depths, velocities and hazard scores in the 2D model extent (defended floodplain). A comparison of pre- and post-development modelled 200-year return period with climate change allowance flood levels in the 1D model extent at key nodes upstream and downstream of the proposed Waterside Campus development are listed in Table 6 for the case that there is no breach of Northampton flood defences. The model results in Table 6 show that post-development flood levels in the River Nene upstream and downstream of the proposed Waterside Campus development are lower than pre-development as a result of Upton FAA. The new bridge has a marginal impact directly upstream where there is a slight and localised increase in modelled floodplain depths (modelled depth increase between 0mm and 20mm) directly upstream of the proposed new bridge. This is considered an insignificant impact as the level increase is marginal and only affects the floodplain adjacent to a car park - which remains dry during the modelled 1000-year with climate change allowance flood for the post-development case (Figures C5 and C6 in Appendix C), and the Waterside Campus development site, for which there will be land raising above the 1000-year with climate change flood level adjacent to the River Nene. Peak level (mAOD) and diff. Compared to pre-devl. case (m) for modelled200-year with climate change allowance flood Location River Nene: Southbridge ISIS ID model node Pre-development (before development of Waterside Campus, Upton FAA and Ransome Road) Post-development A Post-development B (after development of Waterside Campus and Upton FAA but before development of Ransome Road) (after development of Waterside Campus, Upton FAA but and Ransome Road) a7486b1 59.62 59.55 (-0.06) 59.56 (-0.06) River Nene: upstream end of Waterside Campus site a7455 58.74 58.72 (-0.02) 58.72 (-0.02) River Nene: approx. 160m upstream of Nunn Mills sluice a7424a 58.46 58.46 (-0.02) 58.45 (-0.02) Upstream of River Nene bridge a7416b1 57.63 57.65 (+0.02) 57.65 (+0.02) Upstream of Nunn Mills sluice gates a7408as 58.32 58.31 (-0.01) 58.31 (-0.01) Upstream of new River Nene bridge a7403 57.63 57.65 (+0.02) 57.65 (+0.02) a7403i2 57.61 57.58 (-0.04) 57.58 (-0.04) Downstream of new River Nene bridge Table 6: Comparison of pre and post development 200-year flood levels in the ID model extent The defended floodplain in the vicinity of the proposed Waterside Campus development is represented within the 2D hydraulic model extent. The impact of the proposed Waterside Campus development on flooding in the defended floodplain during a breach of Northampton flood defences is discussed in Sections 8.2, 9.1 and Appendix C. 8.2 Breach of Northampton flood defences The proposed Waterside Campus development includes displacement of defended floodplain potential storage due to raising of ground levels within the development site. Whilst these raised levels are in the defended floodplain there is a residual risk that Northampton flood defences are breached or overtop. The proposed defended floodplain displacement results in a loss of potential defended floodplain storage. The mitigation against increased flood risk during a breach of Northampton flood defences is provided by Upton Flood Attenuation Area, which reduces River Nene flood levels and so reduces flows over a breach for a given design return period. This mitigates for the loss of defended floodplain storage is detailed in Section 9.1 and Appendix C. 8.3 Surface water flooding The proposed surface water drainage strategy (Sections 6.2 and 6.3) specifies on-site attenuation of surface water flows limited to be less than pre-development rates for storms up to a 200-year with climate change return period. Surface water flows from the developed site will therefore be lower than those of the existing site. For storms exceeding the drainage capacity surplus flow would be directed overland as described in Section 6.4 and Figure 6. 8.4 Fluvial Morphology The proposed Waterside Campus development will not impact fluvial morphology since the proposed new River Nene bridge and foot/cycle bridge have negligible impact on local hydraulics. 9 Residual Risks 9.1 Breach of Northampton Flood Defences The Waterside Campus development site is mostly in the defended River Nene floodplain and there is a residual flood risk associated with a breach or over-topping of Northampton flood defences. Upton Flood Attenuation Area was implemented upstream of Northampton by the Homes and Communities Agency to mitigate the impacts of development in and around Northampton, including the proposed Waterside Campus development. The impact of the proposed development on the consequences of a breach of Northampton defences, and the mitigation provided by Upton FAA, has been assessed by hydraulic modelling. This breach analysis modelling is reported in Appendix C which concludes that: • • • • • The Environment Agency Upper Nene Strategic 1D-2D Model (2013) has been developed by University of Northampton in 2013 to assess the impacts of the planned Waterside Campus development on flood risk during a breach of Northampton flood defences. This model has been developed further to assess the impact of the proposed Waterside Campus development on flood risk during a breach of Northampton flood defences and during the 1000-year with climate change allowance River Nene flood. The implementation of Upton Flood Attenuation Area has wide spread benefits in terms of reduced flood risk throughout Northampton. The breach modelling undertaken shows that the proposed Waterside Campus development does not result in increased flood risk elsewhere during a breach of Northampton flood defences occurring at the peak level of the 200-year with climate change allowance River Nene flood, except for a marginal impact directly upstream of the proposed new River Nene bridge where there is a slight and localised increase in modelled depths (modelled increase between 0m and 20mm) directly upstream of the proposed new bridge. This is considered an insignificant impact as the level increase is marginal and only affects the floodplain adjacent to a car park - which remains dry during the modelled 1000-year with climate change allowance flood for the post-development case (Figures C5 and C6 in Appendix C), and the Waterside Campus development site, for which there will be land raising above the 1000-year with climate change flood level adjacent to the River Nene. The proposed new access road will provide safe access/egress to the planned Waterside Campus development (and later to the panned Ransome Road development) during a modelled 1000-year return period flood with climate change allowance. The modelling presented demonstrates that Upton FAA provides the required mitigation against increased residual flood risk due to the proposed Waterside Campus development. 9.2 Surface water drainage exceedance flows For storms exceeding the surface water drainage capacity surplus runoff would be routed over land as detailed in Section 6.4 and Figure 6. 9.3 Flood warning and evacuation The proposed new road within the Waterside Campus development is designed to provide emergency access/egress for planned development in the area including the Waterside Campus development site and, when implemented, the Ransome Road development site. The proposed new road will provide safe access/egress during the modelled 1000-year with climate change allowance River Nene flood and during a breach of Northampton flood defences during a modelled 200-year with climate change allowance River Nene flood. The proposed Waterside campus development is close to the existing Environment Agency flood warning siren at the Ransome Road/ London Road junction. 10 EA Strategic Review and Update 10.1 Compliance with EA Strategic Review and Update Tables 7 and 8 demonstrate compliance of the proposed Waterside Campus development with the Environment Agency’s Strategic Review of Development and Flood Risk: Nene Catchment Northampton and Upstream (1999) and its update (2004). Table 7: Strategic Review policies and principles for development in the Upper Nene catchment Policies No. 1 Policy followed by response Development will not be permitted if it would either alone, or in conjunction with other developments, be likely to: • Be itself at risk from flooding; • inhibit the capacity of the floodplain to store water • impede the flow of flood water; and • otherwise increase the flood risk. The proposed Waterside Campus development includes land raising to remove the site from the 200-year return period with climate change allowance modelled flood extent, including with a breach of Northampton flood defences. Finished floor levels will be a minimum of 300mm above the modelled 200year return period with climate change allowance modelled flood level. The proposed new access road and River Nene bridge are designed with an elevation to provides a safe access/egress route during the 1000-year with climate change allowance flood in the River Nene. Section 9.1 and Appendix C describe breach modelling undertaken to demonstrate that Upton Flood Attenuation Area mitigates for increased residual risk due to displacement of floodplain storage by the proposed development. The proposed development will include improvement works where possible to the Hardingstone Dyke, which will be developed in detail with the Environment Agency as part of the Reserved Matters applications as the detailed design develops. The proposed Ransome Road development FRA (Homes and Communities Agency, 2010) includes extending the existing drainage ditch running west-east along the southern side of the railway crossed by the proposed Nunn Mills Road. The Ransome Road FRA specified a 10m wide channel width for this ditch to convey breach flood flows, and this channel width is therefore retained when representing the Ransome Road development in the proposed Waterside Campus development FRA. The Ransome Road development will need its own FRA and ground re-modelling, but the FRA for the Waterside development does not place any more onerous requirements on this site. Modelled flood levels in the River Nene are lower post-development than pre-development upstream and downstream of the proposed development (Table 6). Whilst modelled flood levels are lower post-development upstream and downstream of the proposed Waterside Campus development, the new River Nene bridge results in a slight and localised increase in modelled 200-year return period with climate change allowance flood levels (between 0mm to 20mm) directly upstream of the proposed bridge, reducing to zero approximately 100m upstream in the northern river branch (50m upstream of the existing River Nene bridge) and 50m upstream in the southern branch (at Nunn Mills sluice). This is considered an insignificant impact as the level increase is marginal and only affects the floodplain adjacent to a car park - which remains dry during the modelled 1000-year with climate change allowance flood for the post-development case (Figures C5 and C6 in Appendix C), and the Waterside Campus development site, for which there will be land raising above the 1000-year with climate change flood level adjacent to the River Nene. The proposed development incorporates SUDS surface water drainage systems which are designed to have discharge rates less than pre-development for storms up to a 200-year return period with climate Policies No. Policy followed by response change allowance. 2 Proposals which do increase flood risk, either alone or in conjunction with other development, will be resisted unless appropriate mitigation measures, including suitable maintenance arrangements, are provided, that comply with the requirements of these policies and principles as part of the overall development. Section 9.1 and Appendix C describe breach modelling undertaken to demonstrate that Upton Flood Attenuation Area mitigates for increased residual risk due to displacement of floodplain storage in the defended floodplain. Whilst modelled flood levels are lower post-development upstream and downstream of the proposed Waterside Campus development, the new River Nene bridge results in a slight and localised increase in modelled flood levels (by 0 to 20mm) directly upstream of the proposed bridge, reducing to zero approximately 100m upstream in the northern river branch (50m upstream of the existing River Nene bridge) and 50m upstream in the southern branch (at Nunn Mills sluice). This is considered an insignificant impact as the level increase is marginal and only affects the floodplain adjacent to a car park - which remains dry during the modelled 1000-year with climate change allowance flood for the postdevelopment case (Figures C5 and C6 in Appendix C), and the Waterside Campus development site, for which there will be land raising above the 1000-year with climate change flood level adjacent to the River Nene. The proposed development site will incorporate SUDS surface water drainage systems which are designed to limit runoff rates to pre-development rates for storms up to a 200-year return period with climate change allowance. Section 7.6 and Appendix F provide information relating to maintenance of the proposed sustainable drainage systems (SUDS). 3 Development proposals must incorporate source control techniques and sustainable urban drainage systems. The proposed development incorporates SUDS surface water drainage systems. 4 Development proposals that would result in the restoration and or enhancement of the floodplain or contribute to a reduction in surface water runoff will be encouraged. The proposed development site would incorporate SUDS surface water drainage systems which are designed to limit runoff rates to pre-development rates for storms up to a 200-year return period with climate change allowance. 5 Development proposals must bring about an overall reduction in flood risk. Surface water runoff from the development site would have runoff rates less than or equal to predevelopment rates for storms up to a 200-year return period with climate change allowance. There would therefore be a reduction in flood risk. The Upton Flood Attenuation Area scheme results in lowered flood levels throughout Northampton. Whilst modelled flood levels are lower post-development upstream and downstream of the proposed Waterside Campus development, the new River Nene bridge results in a slight and localised increase in modelled flood levels (by 0 to 20mm) directly upstream of the proposed bridge, reducing to zero approximately 100m upstream in the northern river branch (50m upstream of the existing River Nene bridge) and 50m upstream in the southern branch (at Nunn Mills sluice). This is considered an insignificant impact as the level increase is marginal and only affects the floodplain adjacent to a car park - which remains dry during the modelled 1000-year with climate change allowance flood for the postdevelopment case (Figures C5 and C6 in Appendix C), and the Waterside Campus development site, for which there will be land raising above the 1000-year with climate change flood level adjacent to the River Nene. Principles No. Principle followed by response 1 Development will be directed away from Greenfield sites in the floodplain to prevent any further erosion of its flood flow and flood storage capacity, which would increase flood risk. The Waterside Campus development site is a brownfield site. 2 Any permitted development outside the floodplain will need to include mitigation action against its effects up to at least the same level of storm event governing the existing flood defence standard, this will prevent any future erosion of that standard. Complies. Runoff form the development site limited to pre-development runoff conditions for storms up to a 200-year return period with climate change allowance. 3 Any redevelopment of brownfield sites within the floodplain will only be permitted if there is no increase in flood risk to people and property, and the development maintains or improves river flood defences to at least the accepted defence standard, and if any works required to prevent any future erosion of that standard are carried out where it is relevant to the site. Complies. Runoff from the development site will be limited to pre-development runoff conditions. Benefits in terms of reduced flood levels are realised throughout Northampton by adoption of the Upton Flood Attenuation Area scheme. Whilst modelled flood levels are lower post-development upstream and downstream of the proposed Waterside Campus development, the new River Nene bridge results in a slight and localised increase in modelled flood levels (by 0 to 20mm) directly upstream of the proposed bridge, reducing to zero approximately 100m upstream in the northern river branch (50m upstream of the existing River Nene bridge) and 50m upstream in the southern branch (at Nunn Mills sluice). This is considered an insignificant impact as the level increase is marginal and only affects the floodplain adjacent to a car park - which remains dry during the modelled 1000-year with climate change allowance flood for the post-development case (Figures C5 and C6 in Appendix C), and the Waterside Campus development site, for which there will be land raising above the 1000-year with climate change flood level adjacent to the River Nene. 4 New development must contribute towards a reduction in flood risk. This may be achieved by extra mitigation measures or by contributing to improved floodplain flow or floodplain storage to achieve a progressive reduction to flood risk. Development of the site will improve flood storage through provision of SUDS. Upton Flood Attenuation Area reduces flood levels in Northampton. 5 Appropriate long-term maintenance agreements in respect of all flood risk reduction infrastructure including flood defences, attenuation lagoons, structures and facilities etc. must be completed prior to construction, in order that the long-term effectiveness of these facilities is ensured. The proposed adoption and maintenance arrangements for the proposed development surface water drainage and Sustainable Drainage Systems (SuDS) are in Section 7 of Appendix F: Outline Foul, Surface Water Drainage and SuDS Strategy. 6 A formal Flood Risk Impact Assessment of the potential impacts of any proposed development, detailing flood risk reduction measures to be incorporated, will be required, prior to development taking place. This FRA addresses the issues. 7 All flood risk reduction measures should be completed and operationally effective prior to development commencing. Upton Flood Attenuation Area mitigates for the displacement of floodplain storage and is already in place. 8 In seeking to promote a reduction in flood risk a strategic approach which will both reduce flood risks and provide opportunities for environmental enhancements, should be promoted. The proposed development will incorporate SUDS surface water drainage systems which reduce flood risk by limiting runoff flows from the site. The Upton Flood Attenuation Area scheme benefits a much wider area in Northampton. The site is allocated in an up to date development plan document (the NCAAP) which is informed by a Strategic Flood Risk Assessment. There are a number of significant sustainability benefits arising from redeveloping this brownfield site. Not least, the remediation and biodiversity improvements are considered to be of significant environmental benefit to the area. These significant benefits are considered to outweigh flood risk (especially given that the site is now subject to flood defences). 2. A site-specific flood risk assessment must demonstrate that the development will be safe for its lifetime taking account of the vulnerability of its users, without increasing flood risk elsewhere, and, where possible, will reduce flood risk overall. This document has been prepared by Halcrow and demonstrates that this part of the test has been passed. Conclusion This Sequential Test has been undertaken in order to support the University of Northampton’s planning application for the development of new campus at the Avon/Nunn Mills site, Northampton. It is clear from undertaking this Sequential Test that there are no reasonably available alternative sites to that at Ransome Road/Nunn Mills within the University’s search area (i.e. within close proximity to Northampton town centre). This is an allocated site that needs to be developed. The accompanying Flood Risk Assessment has demonstrated how flood risks will be managed so that the development remains safe throughout its lifetime. Both elements of the Exception Test are also considered to be passed. Appendix B SFRA Level 2 Figures D-6 and D-7 Information Requirement Response Compliance with PPG25 This document complies with current planning policy, NPPF. Statement of compliance with Strategic review and update Strategic Review: Table 7 details compliance with the Strategic Review. Strategic Review update: The proposed development will incorporate SUDS surface drainage systems which will result in limited runoff flows from the site and would therefore contribute towards reduced flood levels in Northampton. Programme of compensation for permanent loss of floodplain Potential loss of defended floodplain is mitigated by Upton Flood Attenuation Area. Modification of model to incorporate impacts and mitigation See Section 9.1 and Appendix C. Legal agreements for future maintenance The proposed adoption and maintenance arrangements for the proposed development surface water drainage and Sustainable Drainage Systems (SuDS) are in Section 7 of Appendix F: Outline Foul, Surface Water Drainage and SuDS Strategy. Statements on contribution to sustainable communities objectives e.g. improvements to infrastructure The proposed development will incorporate SUDS surface water drainage systems. The proposed new road within the development is essential infrastructure to enable planned brownfield site regeneration in Northampton. Table 8: Compliance with Strategic Review Update 11 Conclusions The following conclusions can be drawn from this Flood Risk Assessment report: • This NPPF compliant flood risk assessment demonstrates that the proposed Waterside Campus development will not be at risk of flooding and will not increase the risk of flooding elsewhere. • Whilst modelled flood levels are lower post-development upstream and downstream of the proposed Waterside Campus development, the new River Nene bridge results in a slight and localised increase in modelled flood levels (0 to 20mm) directly upstream of the proposed bridge, reducing to zero approximately 100m upstream in the northern river branch (50m upstream of the existing River Nene bridge) and 50m upstream in the southern branch (at Nunn Mills sluice). This is considered an insignificant impact as the level increase is marginal and only affects the floodplain adjacent to a car park which remains dry during the modelled 1000-year with climate change allowance flood for the post-development case (Figures C5 and C6 in Appendix C), and the Waterside Campus development site, for which there will be land raising above the 1000-year with climate change flood level adjacent to the River Nene. • The current 200-year level of protection provided by Northampton Flood Defences will not be affected by the proposed development. • The surface water drainage strategy for the proposed development will employ sustainable drainage systems (SUDS) designed to limit surface water flows to pre-development rates for storms up to a 200-year return period with climate change allowance. For storms exceeding the drainage capacity surplus runoff will be directed over land as described in Section 6.4. • The proposed adoption and maintenance arrangements for the development surface water drainage and Sustainable Drainage Systems (SuDS) are in Section 7 of Appendix F: Outline Foul, Surface Water Drainage and SuDS Strategy. The drainage system within the Avon site (excluding Avon Building) will be private and will have to be maintained by a private management company. However, the proposed surface water drainage system and SuDS within the Nunn Mills site can be offered for adoption to Anglian Water under the Section 104 Agreement of the Water Industry Act based on the assumption that commercial buildings will be owned by different parties/people. If piped networks are to be offered for adoption to Anglian Water, these will be subject to Easement Agreements along the proposed sewers. If SuDS are offered for this process will involve land ownership transfer from future land owner to Anglian Water. The extent of this will have to be determined through liaisons with Anglian Water. The drainage in the adopted highway will be maintained by the Local Highway Authority as part of its routine maintenance programme to ensure operation of the system. • The loss of defended floodplain due to the proposed Waterside Campus development is mitigated by Upton Flood Attenuation Area, which was constructed ahead of development in and around Northampton as strategic infrastructure to mitigate the impacts of development on flood risk. • Benefits, in terms of reduced flood levels resulting form implementing Upton Flood Attenuation Area, extend over a much larger area in Northampton and are not confined to the development sites linked to the scheme. • A minimum of 5m maintenance easement will be provided adjacent to the River Nene and Hardingstone Dyke. • The new access road will provide safe access/egress to the planned development during a modelled 1000-year return period flood with climate change allowance. • The Waterside Campus site is located close to the existing Environment Agency flood warning siren at the Ransome Road/ London Road junction. 12 References NPPF: National Planning Policy Framework and technical Guidance, Communities and Local Government 2012 PPS25: Development and Flood Risk, Communities and Local Government 2006 Northampton Central Area Action Plan, Northampton Borough Council 2013 Ransome Road Development Site Flood Risk Assessment, Halcrow 2010 (approved FRA of planning application reference 06/0016/OUTWNN) Nunn Mills Road Extension/Upgrade Flood Risk Assessment, Halcrow 2011 (approved FRA of planning application reference 11/0014/FULWNN) Strategic Review of Development and Flood Risk Nene Catchment Northampton and Upstream, EA 1999 Update to the Strategic Review of Development and Flood Risk Nene Catchment Northampton and Upstream, EA 2004 West Northamptonshire Strategic Flood Risk Assessment Level 1, Scott Wilson 2009 West Northamptonshire Strategic Flood Risk Assessment Level 2, Scott Wilson 2010 FD2320: Flood Risk Assessment Guidance for New Development: Phase 2, Defra 2005 FD2321 Flood Risks to People – Guidance Document, Defra 2005 Preliminary rainfall-Runoff Management for Developments R&D Technical Report, Defra 2005 Upton Flood Attenuation Area Phase 3 Reserved Matters Submission, Flood Risk Assessment, English Partnerships July 2007 (Planning application N/2007/0967) Appendix B – SFRA Level 2 Figures D-6 and D-7 Appendix A NPPF Sequential Test for the proposed Relocation of the University of Northampton Appendix A NPPF Sequential Test for the proposed Relocation of the University of Northampton Sequential Test and Exception Test University of Northampton Relocation to Avon/Nunn Mills site Introduction The University of Northampton is seeking to move to the Avon/Nunn Mills site. The reasons for this are set out in Appendix 1 to this document (and elsewhere in the planning application). In short, in order to maximise its prospects for the future the University needs to consolidate its existing split campus operations to a single site. The University has also taken the decision that its new site should be close to (at least within reasonable walking distance of) Northampton town centre. This sequential test has been undertaken in order to support the planning application for the development of the Avon/Nunn Mills site for a new campus plus commercial development. The purpose of a sequential test is to steer new development into areas that are at the lowest probability of flooding, Flood Zone 1. Where there are no reasonably available sites in this zone, reasonably available sites should be considered in Flood Zone 2. Guidance on the Sequential Test is contained within the NPPF and its accompanying technical guidance. Paragraph 101 of the NPPF states that The aim of the Sequential Test “is to steer new development to areas with the lowest probability of flooding. Development should not be allocated or permitted if there are reasonably available sites appropriate for the proposed development in areas with a lower probability of flooding. The Strategic Flood Risk Assessment will provide the basis for applying this test. A sequential approach should be used in areas known to be at risk from any form of flooding” Paragraph 102 states that If, following application of the Sequential Test, it is not possible, consistent with wider sustainability objectives, for the development to be located in zones with a lower probability of flooding, the Exception Test can be applied if appropriate. For the Exception Test to be passed: • it must be demonstrated that the development provides wider sustainability benefits to the community that outweigh flood risk, informed by a Strategic Flood Risk Assessment where one has been prepared; and • a site-specific flood risk assessment must demonstrate that the development will be safe for its lifetime taking account of the vulnerability of its users, without increasing flood risk elsewhere, and, where possible, will reduce flood risk overall. Both elements of the test will have to be passed for development to be allocated or permitted. The key documents upon which this Sequential Test have been based are: • Northampton Central Area Action Plan • The West Northamptonshire Strategic Flood Risk Assessment Final Level 1 Report – Volume 1 • Northampton Level 2 Strategic Flood Risk Assessment Living Document Proposal A full description of the Avon/Nunn Mills site is contained withing the accompanying planning application and EIA. In short, it is a brownfield site formerly used (to the west of Nunn Mills Road) as Avon’s manufacturing and distribution centre and (to the east of Nunn Mills Road) as a power station. Avon’s headquarters building remains within the site (albeit excluded from the University’s planning application). The planning application site itself has something of an unkempt appearance, containing large areas of hardstanding, piles of materials and vacant buildings. The site is bounded to the north by the River Nene and to the south by Hardingstone Dyke and the former Northampton to Bedford railway line (now disused). Again a full description of the development is contained within the accompanying planning application and EIA. The University proposes to construct is academic buildings fronting the River Nene and around a diagonal corridor from the north west to the south central of the site. Student accommodation will be focussed in the south western corner of the site. The east part of the site is proposed for commercial development (office development by a commercial organisation independent of the University), the University’s administration and management functions, plus a hotel, leisure facility and sports pitch. Car parking is generally at grade at a number of locations around the site. Road access is proposed via a new bridge from Bedford Road. A pedestrian bridge is also proposed into the north west corner of the site from Becket’s Park. The Sequential Test in the Context of the University Proposal With regard to the Table 2: Flood risk vulnerability classification of the NPPF technical guidance, the proposal is considered to partly fall within the ‘more vulnerable’ category (university and student accommodation) and the ‘less vulnerable’ category (office and commercial development, plus ancillary university development). The primary flood risk source for this development area is the River Nene, which lies to the north of the site. However, the whole of the area is now defended by the recently completed Northampton Flood defences, designed to provide protection against a 1 in 200 years return period flood event ad Upton Flood Attenuation Area upstream of Northampton. It is understood that the development area, despite being in the Nene floodplain, is classified as Flood Risk Category 2 and 3a. As part of the site is a ‘more vulnerable use’ falls within Flood Risk Category 3a, Table 3 of the NPPF Technical Guide states that the Exception Test must be carried out. Planning Policy Background The Avon Nunn Mills site is allocated in the Northampton Central Area Action Plan 2013 (NCAAP). (This allocation also includes the Ransome Road site to the south of the former railway line.) Whilst the site is allocated for 2000 dwellings and 16000 sq m of office space, paragraph 6.68 of the NCAAP refers to the University and makes clear that educational use on part of the site would be acceptable in principle. The NCAAP also identifies (at para 6.74) that extensive works to increase flood attenuation capacity upstream, west of Upton Valley Way has been undertaken to allow the Avon / Nunn Mills/ Ransome Road developments to proceed. The NCAAP and is predecessor documents were developed from a sound evidence base that included much work on flood risk: - The West Northamptonshire Strategic Flood Risk Assessment Final Level 1 Report – Volume 1 February 2009 sets out the general approach to development in areas of West Northamptonshire affected by flooding. - The Northampton Level 2 Strategic Flood Risk Assessment Living Document refers to the Nunn Mills Road area and states “Any future proposed development should be rolled back from the watercourse. More vulnerable and highly vulnerable development should be located to the south of the area, with less vulnerable and water compatible development being more appropriate towards the north of the area. Due to the orientation of the site in relation to the River Nene, a breach could occur at any point along the defences. This is important to note at site-specific FRA stage as only a single breachhas been considered as part of the Level 2 SFRA.” Table B-1 of this document highlights that NBC accept that “’More Vulnerable’ development is likely. Methodology NPPF paragraph 104 states that “for individual developments on sites allocated in development plans through the Sequential Test, applicants need not apply the Sequential Test.” Appendix C Technical Note: University of Northampton Relocation breach analysis & Modelling Figures The site is allocated for residential and office development. the NCAAP makes clear that educational use on part of the site would be acceptable in principle. This allocation was made in full knowledge of the SFRAs set out above. However, the Environment Agency has stated that a Sequential Test is required because the proposed development (education) differs from the actual allocation within the NCAAP. The proposed methodology for the Sequential Test is based upon the University’s requirements for a new site and the general national planning requirements for major development. The key criteria is as follows: - Site size of at least 20 ha to accommodate University campus The site should be a sustainable site, close to Northampton town centre Development should be in accordance with the Local Development Framework The site should be brownfield The University needs to open for the 2018/19 academic year The site should be within or in close proximity to the Enterprise Zone The University’s clear requirement, and one of the key reasons for its move, is to locate to a site within closer proximity to the town centre. Accordingly, this Sequential Test can only realistically consider sites within the central area of Northampton. If a site was not available close to the town centre, then the University would be highly unlikely to relocate. Accordingly, the Sequential Test considers sites within the Northampton Central Area Action Plan. The key development sites are: - Bus Interchange/Fishmarket Grosvenor Centre Abington Street East Castle Station St Johns Angel Street Bridge Street Upper Mounts/Great Russell Street Spring Boroughs The Waterside: Brampton Branch/St Peters Way The Waterside: Southbridge West The Waterside: Becket’s Park The Waterside: Nene Meadows Market Square Drapery Freeschool Street Former Royal Mail Sorting Office Telephone Exchange, Spring Gardens Site Assessment The scale of site required by the University inevitably has a significant effect upon the site assessment. The University needs to find a campus that can accommodate over 50,000 sq m of development. There needs to be open space in and around the campus to create areas for informal recreation. It also has a preference for expansion space plus a co-location with commercial business development. For these reasons the minimum site size is considered to be 20 ha. Of the NCAAP sites, the Bus Interchange/Fishmarket, Abington Street East, St Johns, Angel Street, Bridge Street, Upper Mounts/Great Russell Street Spring Boroughs, The Waterside: Southbridge West, Market Square, Drapery, Freeschool Street, Former Royal Mail Sorting Office and Telephone Exchange, Spring Gardens are all far to small to be considered as a realistic redevelopment site. The Grosvenor Centre site is larger but is preferred use is retail development. This is the key retail area within Northampton and it is considered that redevelopment for any use other than retail is highly unlikely and not likely to be supported in planning policy terms. Castle Station is smaller than the University would prefer (c12 ha). Planning permission has been granted for the redevelopment of the station and development is underway. For these reasons the site is not considered to be available. The Waterside: Brampton Branch/St Peters Way is a larger site. It has been considered by the University but deliverability given the contamination issues is considered to be questionable. The site is anyway within an area at risk of flooding. The Waterside: Becket’s Park is essentially a Greenfield park. There is a small potential development site on the former railway embankment, but this would be far too small for the Univeristy’s purposes. It is considered highly unlikely that planning permission would be granted for redevelopment of a public park. The site is anyway within an area at risk of flooding. The Waterside: Nene Meadows is essentially an open, greenfield amenity area. It is considered highly unlikely that planning permission would be granted for redevelopment of this largely greenfield site. The site is anyway within an area at risk of flooding. Therefore only the Avon/Nunn Mills site meets the University’s requirements for the development. Exception Test 1. It must be demonstrated that the development provides wider sustainability benefits to the community that outweigh flood risk, informed by a Strategic Flood Risk Assessment where one has been prepared There are a large number of wider sustainability benefits arising from the proposal. The relocation of the University to a more sustainable (town centre) site is a key aspiration supported by the Borough Council and West Northampton Development Corporation. The University is a key employer within the town and a key contributor towards the vitality of Northampton as a whole. The retention of a strong University within the town and in a more sustainable location is considered to have a major beneficial impact upon the social and economic well being of the town centre. As set out elsewhere in the planning application, the University needs to pursue this relocation in order to remain competitive. The University considers that to ‘do nothing’ is not an option. To retain a University within the town is considered to enhance the viability of Northampton, which in turn enhances the sustainability of the entire Borough and wider County. The Avon/Nunn Mills site has remained undeveloped for years. It is contaminated, with poor road access (the existing access bridges have a weight restriction). The existing power station needs to be relocated and new services provided across the site. The site overall has the potential to become an environmental issue for the town if it is not developed. The overall development proposal will remediate the site, with a programme of works to be agreed with the EA, which is a clear sustainability benefit. A number of biodiversity improvements are also proposed. The site is allocated for development and lies within the Enterprise Zone. It is understood that all the key stakeholders, including the Borough Council, WNDC, the County Council and the Enterprise Zone support the development. It is also understood that the Environment Agency supports the redevelopment in principle. An additional benefit of the University’s development is that it will create development plots for commercial business development. These will benefit from the overall remediation programme, the new access and the campus environment. It is highly unlikely that they could be delivered alone. The commercial business development will clearly create employment opportunities for the town and surrounding area and within the Enterprise Zone. Appendix C – Technical Note: University of Northampton Relocation breach analysis & Modelling Figures Halcrow Group Limited Burderop Park, Swindon, Wiltshire SN4 0QD tel 01793 812479 fax 01793 812089 halcrow.com Technical note Project Northampton University Relocation FRA Subject Hydraulic Modelling Author Feifei Leighton/Robert Bird Date Ref 15 August 2013 203239 Prepared by Date Checked by Date Approved by Date Halcrow Group Limited is a CH2M HILL company Northampton University Relocation FRA: Hydraulic modelling 1 Page 2 of 21 Introduction This technical note is an appendix to the flood risk assessment for the proposed relocation of Northampton University to the Northampton Waterside Campus (also known as the Avon/Nunn Mills Road site) and reports hydraulic modelling undertaken to assess the residual flood risk associated with a breach of Northampton flood defences, and the impact of a 1000-year flood with climate change allowance on the proposed development. The proposed development layout is shown in Figure 1.1. The proposed development site lies mostly in the defended River Nene flood plain in Northampton. The development involves: • Raising site levels above the modelled 200-year return period with climate change allowance flood level as indicated in Figure 3.4 – and for some areas above the 1000-year return period with climate change allowance flood level . Construction of university buildings and facilities, and commercial buildings, as shown in the proposed Masterplan in Figure 1.1. Construction of a new road crossing the development site connecting Bedford Road to Ransome Road as shown in Figure 1.1. The new road will include a new bridge crossing the River Nene and openings to accommodate existing drainage channels in the vicinity of the disuse railway at the southern edge of the proposed Northampton University Waterside Campus site. New foot/cycle bridge • • • The impact of the proposed development on the consequences of a breach of Northampton flood defences has been assessed by hydraulic modelling. The locations of simulated breaches were originally agreed in consultation with the Environment Agency to be locations 1 and 2 shown in Figure 1.2. However, the proposed land raising of the site is at a level above the modelled River Nene 200-year with climate change allowance flood level. Breaches at these locations would therefore not occur and so have not been simulated. In additional to the breach locations agreed with the Environment Agency, a breach has been simulated at the Carlsberg sluice gate upstream of Southbridge. A breach at this location was simulated for the Ransome Road development site FRA and the same breach parameters have been adopted for this assessment (i.e. same breach width, depth and with breach occurring at time of peak river level). The modelling has the following objectives: • To assess the impact of the proposed development on flood risk elsewhere including following a breach of Northampton flood defences, during a 200-year with climate change allowance flood in the River Nene, both with and without implementation of the approved outline design for the development of the Ransome Road site (Ransome Road Flood Risk Assessment, Homes and Communities Agency 2010). • To show that the proposed new road provides safe access and egress (low flood risk category in Defra R&D Technical Report FD2320/TR2 and the May 2008 EA/HR Wallingford supplementary guidance note) along its length during a 1000-yr with climate change flood event (without a breach of Northampton flood defences), both with and without implementation of the approved outline design for the development of the Ransome Road site (Ransome Road Flood Risk Assessment, Homes and Communities Agency 2010). WATERSIDE CAMPUS MASTERPLAN TOWN CENTRE 1 BECKET`S PARK BEDFORD ROAD 1 NEW FOOT/CYCLE BRIDGE 2 SOCIAL BUILDING 20 MARINA 3 ACADEMIC FACILITIES SPECIALIST SPACE 4 STUDENT RESIDENCES 19 5 LIBRARY/STUDY 6 SHARED TEACHING RIVER NENE 7 CONFERENCE FACILITY 2 8 HEALTH/FITNESS GYM 3 9 VISITOR RECEPTION/ADMINSPACE 18 4 10 ACADEMIC RESEARCH SPACE 13 13 13 11 ENERGY CENTRE 4 12 HOTEL 13 COMMERCIAL OFFICE 4 17 14 COMMERCIAL PARKING 4 5 6 9 15 SPORTS PAVILION 15 12 16 SPORTS PITCHES 4 14 17 UNIVERSITY PARKING 18 AVON COSMETICS HQ 7 4 4 10 4 14 19 NEW ROAD/FOOT/CYCLE BRIDGE 20 EXISTING BRIDGE ACCESS 17 8 17 11 21 ELECTRICAL SUBSTATION EXISTING RAILWAY / SUSTAINABLE TRANSPORT CORRIDOR 16 21 Northampton University Relocation FRA: Hydraulic modelling Breach location 2: approx. grid ref: 475965 259865 Page 3 of 21 Breach location 1 (NN17): approx. grid ref: 476145 259859 New Avon HQ building Figure 1.2: Originally agreed breach locations 2 Scenarios assessed 2.1 Breach scenarios Following the proposed development, the potential for breaching of the River Nene flood defences along the northern edge of the development site is removed as ground levels adjacent to the defences will be raised above the 1000-year with climate change allowance flood level. A breach along the northern edge of the development site has therefore not been simulated. During the Ransome Road application FRA (Homes and Communities Agency, 2010), in consultation with the Environment Agency, the most likely location for a breach that would cause significant flooding at the Ransome Road site was identified to be at Carlsberg sluice, upstream of Southbridge (Breach 09 in the Environment Agency’s River Nene breach modelling). The sluice is 4m wide and lies within Northampton sheet piling flood defences. This assessment considers the impact of the proposed site design on the consequences of a breach of Carlsberg sluice gate (Breach 09). Carlsberg sluice (Breach 09) is a structure designed to retain water. Assuming the structure is adequately maintained the probability of the modelled breach occurring (i.e. failure of the sluice gate during the 200year return period River Nene flood) is therefore considered to be much lower than 0.005 per annum (much lower than once in 200 years) since the modelled breach requires both a 200-year flood level (with climate change allowance) and failure of the structure. A breach of Carlsberg sluice (Breach 09) has been modelled, as in the Ransome Road FRA project and subsequent Nunn Mills Road FRA project, with a 4m wide breach commencing at the peak river level. Northampton University Relocation FRA: Hydraulic modelling Page 4 of 21 The models were run to assess the consequences of a breach of Northampton defences, during a 200-year with climate change allowance flood in the River Nene, for Breach 09, for the development scenarios listed in Table 2.1. 2.2 Development scenarios Upton Flood Attenuation Area (FAA), upstream of Northampton, was implemented by the Homes and Communities Agency (formerly English Partnerships) as strategic flood risk mitigation infrastructure to mitigate flood risk associated with planned development in and around Northampton, including the proposed Northampton University Waterside Campus site development. Upton FAA was implemented ahead of the planned development to provide the required mitigation ahead of development. When assessing the impact of the proposed development on flood risk, the pre-development scenario is therefore considered to be before implementation of Upton FAA. The pre-development scenario is before Upton FAA, Ransome Road development and Northampton University Waterside Campus development. Post-development Scenario A is with the Upton FAA, without Ransome Road development and with Northampton University Waterside Campus development, i.e. the situation if the Northampton University Waterside Campus development is implemented before the Ransome Road Development. Post-development Scenario B is with Upton FAA, with Ransome Road Development and with the Northampton University Waterside Campus development, i.e. the final post ‘all development’ scenario. Northampton University Relocation FRA: Hydraulic modelling Development Scenario Page 5 of 21 Includes Upton FAA? Includes Northampton University Waterside Campus development & new road design? Includes Ransome Road development? Description/Purpose Predevelopment Base Case Pre-development baseline case Current Situation Pre-development current situation case Postdevelopment Scenario A Postdevelopment Scenario B Required to assess the impact of the proposed Northampton University Relocation development and the proposed new road on flooding relative to the pre-development baseline case (including for a breach of Northampton flood defences during the 200yr CC flood), and to show the proposed new road is passable with no more than a ‘low’ (green) flood hazard score during a 1000yr with climate change allowance River Nene flood. Table 2.1: Development scenarios 2.3 Scenarios to assess safe access/egress along the proposed new road The post-development A and post-development B scenarios were run for the design 1000-year with climate change allowance flood, without a breach of Northampton flood defences, to demonstrate that there would be safe access/egress along the proposed new road during the modelled 1000-year return period with climate change allowance flood. Safe access has been defined as a maximum of ‘low’ flood hazard score along the access route. Northampton University Relocation FRA: Hydraulic modelling 3 Hydraulic Modelling 3.1 Model Development 3.1.1 Available models and data Page 6 of 21 The Environment Agency (EA) Upper Nene Strategic 1D-2D Model (2013) has been adapted to investigate the impact of the proposed Northampton University Waterside Campus development on flood risk. Other available models and data for this assessment include: • • • • 3.1.2 Northampton University Waterside Campus topographic survey data (2012) Nunn Mills Road FRA modelling (WNDC 2011), supporting topographic survey data and reports Ransome Road FRA modelling (HCA 2010), supporting topographic survey data and reports Development Masterplan and road design Representation of pre-Upton Flood Attenuation Area scenarios The EA Upper Nene Strategic 1D-2D Model (2013)) represents the Upper Nene catchment with Upton Flood Attenuation Area (FAA) implemented. The pre-Upton FAA model was developed by substituting the EA model representation in the vicinity of Upton FAA (all within the 1D model domain upstream of Northampton) with the pre-Upton FAA representation applied in the Ransome Road FRA (2010) and Nunn Mills Road FRA (2011), for which the modelling was reviewed and approved by the Environment Agency. The upstream and downstream limits for this substitution are 1D ISIS model nodes kis033d (upstream limit) and s23a (downstream limit). The connections to spills and reservoirs were checked to ensure the resulting pre-Upton FAA model has the correct representation. Figures 3.1 and 3.2 show the pre- and post-Upton FAA 1D model schematisation, with model units within the area subject to model changes highlighted in red. Northampton University Relocation FRA: Hydraulic modelling • Page 17 of 21 Ransome Road proposed housing area access road - existing land levels raised by a maximum of approximately 0.13m to remove low spots and so reduce the flood hazard score for access/egress. Extension of existing drainage channel Land grading Land raising for access road Land raising Localised raising of Ransome Road Figure 3.9: Model schematisation of the proposed Ransome Road site land raising 3.1.6 Truncation of Hardingstone Dyke in 1D Model The model was found to produce unstable model results (oscillations) along the Hardingstone Dyke branch of the 1D ISIS model, for both the 200-year with climate change allowance and 1000-year with climate change allowance design floods, caused by large volumes of water flowing across/over the dyke from the River Nene, which caused problems with the 1d/2d link. This instability could cause inaccurate model results in both the 1D domain and the 2D domain floodplain representation. Hence, the representation of Hardingstone Dyke has been truncated in the 1D ISIS model at ISIS node sec016, in order to give stable water levels and so a better representation of flood risk. The truncated section of Hardingstone Dyke was not represented in the 2D domain. A similar model stability issue was highlighted in the Nunn Mills Road Flood Risk Assessment modeling (2011) in which Hardingstone Dyke was truncated (to ISIS node sec016) for the 1000-year with climate change allowance model runs. The truncation of Hardingstone Dyke in the 1D model domain without a corresponding representation of the dyke in the 2D domain is considered conservative in terms of assessing flood risk. For the 1000-year return period with climate change allowance model runs (required to assess access/egress safety along the proposed new road) omitting Hardingstone Dyke acts to increase modelled flood levels. For the 200year return period with climate change allowance model runs there is no modelled floodplain flow in the vicinity of Hardingstone Dyke and so results are not affected by the omission of Hardingstone Dyke Northampton University Relocation FRA: Hydraulic modelling Page 18 of 21 (other than a slightly earlier arrival of Hardingstone Dyke fluvial design flows into the River Nene downstream). The truncation of Hardingstone Dyke therefore results in a model with stable peak water levels and a better representation of flood risk. 3.1.7 Breach Representation A breach of Carlsberg sluice (Breach 09) has been modelled, as in the Ransome Road FRA project, with a 4m wide breach commencing at the peak river level (note different breach timing pre- and postimplementation of Upton FAA). The breaching of Carlsberg sluice (Breach 09) was represented in the hydraulic model for the Northampton University Waterside Campus assessment exactly as it was in the Ransome Road FRA modelling. The model uses a 10m surface elevation grid size. In order to represent a 4m breach, a single grid cell (10m length) was lowered so that elevations at the breach point matched those of immediately adjacent land behind the defence. This land lowering was applied at the time of peak in-channel water level and occurs instantaneously. A flow constriction unit was then used to restrict flow passing through the grid cell by 60%, thereby reducing the 10m wide land lowering to a 4m wide breach flow path. The timing of the breach was set to occur at the peak River Nene level (at ISIS 1d node a7492) as follows: 3.2 • T = 35 hour for Pre-development Base Case • T = 37 hour for Current Situation, Post-development Scenarios A and B Model Run Schedule The following model runs were developed based on the development scenarios described in Section 2.2: Model Return Period Development Scenario 200yr CC no breach 200yr CC breach 09 1000yr CC no breach Pre-development Base Case Current Situation Post-development Scenario A Post-development Scenario B Table 3.2: Model run schedule 4 Model Results 4.1 Flood Hazard outputs The flood hazard classification was calculated in TUFLOW (UK flood hazard, ‘ZUK0’) according to Defra R&D Technical Report FD2320/TR2 and the May 2008 EA/HR Wallingford supplementary guidance note. The flood hazard rating (HR) was calculated according to the following formula from these reports. HR = d x (v + 0.5) + DF (d = depth of flooding, v = velocity of flooding and DF = Debris factor) Northampton University Relocation FRA: Hydraulic modelling Page 7 of 21 Figure 3.1: Pre-Upton FAA 1D model schematisation (model units highlighted in red are within the area subject to model changes) Northampton University Relocation FRA: Hydraulic modelling Page 8 of 21 Figure 3.2: Post-Upton FAA 1D model schematisation (model units highlighted in red are within the area subject to model changes) 3.1.3 Representation of the Northampton University Waterside Campus development and proposed new road The Waterside Campus development Masterplan is shown in Figure 1.1. The land within the development site will be raised to levels above the modelled 200-year with climate change allowance flood level as indicated in Figure 3.3, except at the Avon HQ, the vicinity of the listed engine shed and the existing electricity substation where levels are to remain the same. Some areas will actually be raised above the 1000-year with climate change allowance flood level (see results plots in Figures C1 to C13). The finished ground levels within the site are specified on a 5mx5m resolution grid which is then converted to an ascii grid (.txt) format using the Vector Operations tool in ISIS Mapper. This grid was used to update any change to the ground level that fall onto the 2D surface grids which are specified by 10mx10m cells. The new road design consists of the construction of a new access road east of the existing Nunn Mills Road and modifying levels of the existing Bedford Road. To represent the new road design in the model, design levels specified as points in a .csv file format have been converted to an ascii grid .txt format. The new road design is represented in the model as a z-shape file with 20-m width along the road centrelines which are joined by points at the design elevation. The design levels are specified along the road Northampton University Relocation FRA: Hydraulic modelling Page 9 of 21 centrelines at regular intervals (with automatic interpolations in between the points). Figure 3.5 shows road centrelines of the new road design and Figure 3.6 shows the plan view and long section of the new road design and the culverts/opening underneath. The design for proposed foot/cycle bridge has not yet been finalised but it will be a clear span with soffit levels above the 1000-year return period with climate change allowance flood level (at least 3m above normal water level to meet navigation requirements) and designed to have no negative impact on flood risk compared to the base case model (i.e. Upton Flood Attenuation Area provides mitigation). Figure 3.7 shows the design of the proposed foot/cycle bridge. The proposed buildings shown in Figure 1.1 are represented a local 0.3m increase in ground levels, as has been dome elsewhere in the EA model. This acknowledges that for higher depths buildings may allow some conveyance of flood water e.g. through doors and windows. Figure 3.3 Extent of land raising within the Northampton Waterside Campus Northampton University Relocation FRA: Hydraulic modelling Figure 3.4 New road design centreline and locations of culverts/openings under the road Page 10 of 21 Northampton University Relocation FRA: Hydraulic modelling Page 19 of 21 The debris factor was selected as described in FD2320 and its supplementary guidance note, i.e. DF = 0.5 if d≤0.25m and DF = 1 if d>0.25m or v>2m/s (TUFLOW ‘conservative’ approach). The flood hazard ratings are classified into the flood hazard categories shown in Table 4.1, and these were reflected in the Flood Hazard maps. Flood hazard Rating Flood Hazard Category Description < 0.75 Low Caution - “Flood zone with shallow flowing water or deep standing water” 0.75 - 1.25 Moderate Dangerous for some (i.e. children) “Danger: Flood zone with deep or fast flowing water” 1.25 – 2.0 Significant Dangerous for most people - “Danger: flood zone with deep fast flowing water” > 2.0 Extreme Dangerous for all - “Extreme danger: flood zone with deep fast flowing water” Table 4.1: Flood Hazard Classification from Supplementary Guidance Note. 4.2 Model results maps Maps have been constructed to show the maximum depth, flood hazard and velocity in the study area. Flood depth and velocity grids have been coloured so that the variation across the study area can be clearly seen. Flood hazard grids have been coloured according to the hazard categories in the Defra R&D Technical Report (FD2320/TR2) and as described in Table 4.1 (green = low hazard, yellow = moderate hazard, orange = significant hazard and red = extreme hazard). Modelled maximum depths, velocities and hazard scores for an occurrence of breach 09 during the 200year with climate change River Nene flood are shown in Figures C.1 to C.4 for the Pre-development Base Case, Current Situation, Post-development A and Post-development B scenarios respectively. Modelled maximum depths, velocities and hazard scores during the 1000-year with climate change River Nene flood, without a breach of Northampton flood defences, are shown in Figures C.5 and C.6 for the Post-development A and Post-development B scenarios respectively. Figures C.5 and C.6 are to demonstrate that the proposed new road would be operable during a 1000-year return period flood (rather than for comparison with pre-development scenario model results). Maps showing the difference in maximum depth, hazard and velocity in the study area during a breach of Northampton flood defences, as a result of the proposed development, have also been produced. The differences were calculated by subtracting the post-development results from the pre-development results. A reduction in value as a result of the Northampton university Relocation development is shown as a negative change and vice-versa. A reduction in flood risk has been coloured green on the maps and an increase has been coloured red. Figures C.7 and C.8 show differences (compared to the pre-development Base Case) for an occurrence of Breach 09 during the 200-year with climate change allowance River Nene flood for the Post-development A and Post-development B scenarios. Northampton University Relocation FRA: Hydraulic modelling Page 20 of 21 Model results for the simulated 200-year with climate change allowance River Nene flood without a breach of Northampton flood defences are shown in Figures C.9 to C.13 as follows: • • • • • 4.3 Figure C.9: Maximum flood depths, hazard scores and velocities for the Pre-development Base Case Figure C.10: Maximum flood depths, hazard scores and velocities for Post-development A scenario Figure C.11: Maximum flood depths, hazard scores and velocities for Post-development B scenario Figure C.12: Difference in maximum flood depths, hazard scores and velocities compared to the Pre-development Base Case for the Post-development A scenario Figure C.13: Difference in maximum flood depths, hazard scores and velocities compared to the Pre-development base case for the Post-development B scenario Interpretation of Results Figures C7 and C8 show that, for an occurrence of Breach 09, the mitigation provided by Upton FAA results in a widespread reduction in flood risk hazard score and depth. For the post-development cases A and B (pre-and post-Ransome Road development), in the vicinity of the proposed Waterside Campus development, Figures C7 and C8 show a reduction in flood depth, hazard and velocity. For the postdevelopment cases A and B Figures C7 and C8 show a few model pixels with increases in hazard score along the Delapre Brook alignment compared to the pre-development scenario. However, the modelling shows an overall reduction in depth, hazard and velocity along Delapre Brook and these localised increases are considered modelling artefacts due to e.g. model convergence. Figure C8 shows an increase in hazard score along the breach alleviation routes (extended railway ditch and land graded towards the extended railway ditch) included in the Ransome Road development design. These alleviation measures were considered appropriate by the Environment Agency as part of the Ransome Road flood mitigation design. Figure C8 also shows an increase in hazard score on Ransome Road where the hazard score increases from dry (no hazard score) to Low (comparing Figures C1 and C4). This slight increase during a breach scenario is related to the assumed Ransome Road development outline design (taken from the Homes and Communities Agency Ransome Road FRA modelling, 2010), which will be refined during the detailed Ransome Road development design to satisfy flood risk assessment requirements. Figures C8 and C9 show a single pixel with increased hazard score on the north bank floodplain of the River Nene between the proposed new River Nene bridge and the existing Nunn Mills Road River Nene bridge. This is due to a slight and localised increase in modelled depths (modelled increase between 0m and 10mm) directly upstream of the proposed new bridge. This is considered an insignificant impact as the level increase is marginal and only occurs in the floodplain adjacent to a car park - which remains dry during the modelled 1000-year with climate change allowance flood for the post-development case (Figures C5 and C6). Figures C5 and C6 show modelled maximum depths, hazard scores and velocities along the proposed new access road alignment during a modelled 1000-year return period flood with climate change allowance, for the post-development cases A and B respectively. Figures C5 and C6 show that the proposed access road would provide safe access/egress (max hazard score ‘very low’) during the modelled 1000-year return period flood with climate change allowance, for the post-development cases A and B respectively. The Waterside Campus application does not include the part of the new road south of the Avon/Nunn Mills development site but this has been included in the modelling to demonstrate that the required future road extension to the Ransome Road site is viable in terms of flood risk. Northampton University Relocation FRA: Hydraulic modelling Page 14 of 21 Width (m) Height (m) Length (m) Invert Level (mAOD) Culvert 1 7.7 3.4 23.5 55.0 Culvert 2 10 3.4 20 55.0 Culvert 3 10 3.3 17.5 55.0 Table 3.1 Dimensions and parameters of the three culverts/openings under the new road The four coefficients are set as those suggested in the TUFLOW User Manual: 3.1.4 • The height contraction coefficient is set to 0.6 for square edged box culverts. • The width contraction coefficient is set to 0.9 for sharp edged box culverts. • The general entry loss coefficient as specified by the manufacturer. The value of 0.5 recommended in the TUFLOW User Manual has been used. • The exit loss coefficient (normally recommended as) 1.0 has been used. Representation of Delapre Brook and existing railway drainage ditch As part of the proposed Ransome Road development FRA modelling, some revisions were made to the pre-development hydraulic model to improve detail in the vicinity of the proposed Ransome Road development. The same revisions have been applied to the current Northampton University Relocation FRA model. These changes are listed below and illustrated in Figure 3.7. • • Representation within the model of Delapre Brook (running from west to east, south of the proposed development site). The channel was represented using 1D ESTRY sections with channel cross sections derived from Homes and Communities Agency topographic survey. The Mencap access bridge which crosses this watercourse was also incorporated, taking bridge details from drawings submitted as part of the flood risk assessment for the bridge. Including within the model an existing drainage channel which runs from west to east immediately south of the railway and along the northern edge of the proposed Ransome Road development site. The channel was represented by lowering the 2D surface grid elevations by 1m along the channel alignment (with an improvement made to the previous Ransome Road FRA modelling by using topographic survey data to set the channel bed level rather than applying a constant 1m lowering of original DTM ground levels along the ditch alignment). Northampton University Relocation FRA: Hydraulic modelling Page 21 of 21 Figures C12 and C13 show that Upton Flood Attenuation Area mitigates for the proposed Waterside Campus development for the case without a breach of Northampton flood defences. For the Postdevelopment B case, there are localised increases in flood risk associated with the assumed outline Ransome Road development design as discussed above. 5 Conclusions The Environment Agency Upper Nene Strategic 1D-2D Model (2013) has been developed by Northampton University in 2013 to assess the impacts of the planned Waterside Campus development on flood risk during a breach of Northampton flood defences. This model has been developed further to assess the impact of the proposed Waterside Campus development on flood risk during a breach of Northampton flood defences and during the 1000-year with climate change allowance River Nene flood. The implementation of Upton Flood Attenuation Area has wide spread benefits in terms of reduced flood risk throughout Northampton. The breach modelling undertaken shows that the proposed Waterside Campus development does not result in increased flood risk elsewhere during a breach of Northampton flood defences occurring at the peak level of the 200-year with climate change allowance River Nene flood, except for a marginal impact directly upstream of the proposed new River Nene bridge where there is a slight and localised increase in modelled depths (modelled increase between 0m and 10mm) directly upstream of the proposed new bridge. This is considered an insignificant impact as the level increase is marginal and only occurs in the floodplain adjacent to a car park - which remains dry during the modelled 1000-year with climate change allowance flood for the post-development case (Figures C5 and C6). The proposed new access road will provide safe access/egress to the planned Waterside Campus development (and later to the panned Ransome Road development) during a modelled 1000-year return period flood with climate change allowance. The modelling presented demonstrates that Upton FAA provides the required mitigation against increased residual flood risk due to the proposed Waterside Campus development. Maximum Depth (m) 0 - 0.25 0.25 - 0.5 0.5 - 1.0 1.0 - 2.0 >2.0 1d model area Land raising Buildings post development Proposed road " Breach 09 location Maximum Hazard 0 - 0.75 0.75 - 1.25 1.25 - 2.0 >2 1d model area Land raising Buildings post development Proposed road " Breach 09 location Maximum Velocity (m/s) 0 - 0.25 0.25 - 0.5 0.5 - 1.0 1.0 - 2.0 >2.0 1d model area Land raising Buildings post development Proposed road " Breach 09 location Figure C1: 200 year CC Breach 09 Pre-development Base Case Scenario (without UFAA, without RRD and without NUR) Northampton University Relocation FRA: Hydraulic modelling Page 15 of 21 Existing drainage channel Delapre Brook Mencap bridge Figure 3.7: Amendments to model representation to improve local detail As well as the changes listed above, a small stability patch was added to the current model in the area just downstream of Delapre Brook. This stability patch increases the material friction factor within the area defined from default values (0.06 for farm lands, 0.04 for water courses and 0.045 for urban areas) to 0.15, which removes or reduces instabilities caused by interaction of the 1D and 2D domains. The location of stability patch is shown in Figure 3.8. Northampton University Relocation FRA: Hydraulic modelling Page 16 of 21 Figure 3.8 Stability patch added at downstream end of Delapre Brook to remove model instabilities 3.1.5 Representation of the Ransome Road development The proposed Ransome Road development land raising and associated works was represented in the relevant model scenarios as it was in the Ransome Road FRA project, as detailed below and as illustrated in Figure 3.9: • 2D surface grid elevations raised within the areas of proposed land raising. • Existing railway drainage channel extended along the northern edge of the site (by lowering model 2D domain grid cells). • Land graded in the north-western corner of the development site to encourage overland flow towards the drainage channel. • Local raising of Ransome Road by a maximum of 0.61m to remove low spots and so reduce the flood hazard score for access/egress. Maximum Depth (m) 0 - 0.25 0.25 - 0.5 0.5 - 1.0 1.0 - 2.0 >2.0 1d model area Land raising Buildings post development Proposed road " Breach 09 location Maximum Hazard 0 - 0.75 0.75 - 1.25 1.25 - 2.0 >2 1d model area Land raising Buildings post development Proposed road " Breach 09 location Maximum Velocity (m/s) 0 - 0.25 0.25 - 0.5 0.5 - 1.0 1.0 - 2.0 >2.0 1d model area Land raising Buildings post development Proposed road " Breach 09 location Figure C2: 200 year CC Breach 09 Pre-development Current Situation Scenario (without UFAA, without RRD and without NUR) Maximum Depth (m) 0 - 0.25 0.25 - 0.5 0.5 - 1.0 1.0 - 2.0 >2.0 1d model area Land raising Buildings post development Proposed road " Breach 09 location Maximum Hazard 0 - 0.75 0.75 - 1.25 1.25 - 2.0 >2 1d model area Land raising Buildings post development " Breach 09 location Proposed road Maximum Velocity (m/s) 0 - 0.25 0.25 - 0.5 0.5 - 1.0 1.0 - 2.0 >2.0 1d model area Land raising Buildings post development Proposed road " Breach 09 location Figure C3: 200 year CC Breach 09 Post-development Scenario A (with UFAA, without RRD and with NUR)