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PMG
Radyr Court RoadDanescourt
Drainage Strategy
June 2018
REPORT CONTROL
Document: Drainage Streategy
Project: Radyr Court Road, Drainage Strategy
Client: PMG
Job Number: 173674
File Origin: /tt/file_convert/5bb6f22409d3f2f06e8cb9b0/document.docx
Document Checking:
Primary Author Keith Mortimer Initialled: KM
Contributor Initialled:
Review By Leigh Fotiadis Initialled: LF
Issue Date Status Checked for Issue
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Contents
1 INTRODUCTION............................................................................................................1
2 EXISTING SITE...............................................................................................................2
Site Location................................................................................................................2Site Description..................................................................................................2Existing Drainage Network..................................................................................3River and Watercourses......................................................................................3
3 SURFACE WATER DRAINAGE STRATEGY........................................................................4
Discharge to a Watercourse.........................................................................................4Discharge to a Storm Sewer.........................................................................................4
4 PROPOSED FOUL WATER DRAINAGE STRATEGY............................................................5
Proposed Foul Flow......................................................................................................5Foul Calculations..........................................................................................................5Foul Water Drainage Strategy......................................................................................5
5 CONCLUSIONS AND RECOMMENDATIONS....................................................................6
Figures
Figure 1.1 - Site Location
Appendices
Appendix A - Illustrative MasterplanAppendix B - Welsh Water Maps and LetterAppendix C - NRW Indicative Flood Maps (including Q100 and Q1000 Flood Extent)
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1 INTRODUCTION
1.1 Vectos has been commissioned by PMG to undertake a High-Level Drainage Strategy for the
proposed development at Radyr Court Road, Danescourt.
1.2 The site is currently greenfield. Development proposals include the construction of circa 40
residential dwellings, all necessary highways, private drives, gardens and an area to be
transferred to Cardiff County Council to be used for informal open space.
1.3 This report considers the risk of flooding at the application site and assesses any impact to
the surrounding catchment resulting from proposed developments. The report also
considers viable methods for the disposal of both surface and foul water.
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2 EXISTING SITE
Site Location
2.1 The site is located within Danescourt, an outer suburb of western Cardiff. It is some 2.4km to
the south of Radyr and some 2.8km to the north of Fairwater. The site is also located approx.
5.3 km north of the centre of Cardiff.
2.2 The site is bound to the west by residential properties at Danescourt, to the north and east
by the River Taff, Taff Trail, railway line and green land and to the south by further residential
properties and open green land.
2.3 Figure 1.1 indicates the site location in a local context.
Figure 1.1 – Site Location
Site Description
2.4 The site is currently Greenfield. The topographical survey shows that the site falls from north
to south with levels ranging from approximately 34m AOD to the south and 24m AOD to the
north.
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Existing Drainage Network
2.5 The Welsh Water sewer Maps confirm that there is 4 sewers flowing from north to south
within the site. These are grouped in two with a single foul and a single storm sewer forming
each group of sewers. The most southerly group of sewers consists of a 225 mm foul and a
450mm diameter storm. The second most northerly group of sewers consists of a 525mm
storm sewer and a 375mm foul. Both foul sewer runs lead into a common foul system south
of the development. Similarly, this also is the case for the surface water sewers. The
proposals would be to converge and combine the two foul and the two surface water sewers
under a diversion with DCWW. This will be done under a Section 185 of the water industry
act.
2.6 DCWW have provided a connection point for the foul sewers only. Refer to Appendix B.
River and Watercourses
2.7 The TAN 15 DAM flood map indicates that the River Taff is located along the north-western
boundary of the site. The site boundary is delineated by the railway to which this main river
runs parallel to. The River Taff is categorised as a main river by Natural Resources Wales and
the Welsh Government.
2.8 The site is not affected by fluvial and/or tidal flooding and therefore is considered as flood
free from these sources of flooding. The site is considered to have been flooded in the past
but only from surface water flooding. The TAN 15 categorisation of this site is zone B areas
to be known to have flooded in the past. However, the development proposals are
considered acceptable under TAN 15. Any surface water flooding will be managed at detail
design and will be catered for by the drainage proposals. These proposals might not alleviate
the issue fully but will provide a betterment in the general vicinity and will not pose a risk to
the new development proposals whilst also ensuring that the flood risk is not increased on
any of the neighbouring and existing developments.
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3 SURFACE WATER DRAINAGE STRATEGY
3.1 The site is currently greenfield. All flows generated from single or multiple dwellings would
drain naturally and will be managed at source. It is suggested in the Site Investigation report
undertaken by IG that suitable infiltration is achieved and depth. Therefore, in order to deal
with surface water at source it is proposed that soakaways are used.
3.2 Should these methods above not be achievable, a hierarchy would be followed and where
practical follow the discharge of surface water to the Watercourse and then lastly to a sewer.
3.3 Detailed soakaway testing should be carried out to determine the exact depth and locality of
these soakaways.
3.4 Soakaway testing should be undertaken in accordance with BRE365.
Discharge to a Watercourse
3.5 The river Taff flows from north to south along the eastern boundary of the application site.
3.6 There is an existing storm drain constructed leading towards the River Taff past the
application site, it is assumed that this storm sewer flows into the River Taff.
3.7 If it is found that this sewer does not connect into the River Taff or does not have the
capacity to accommodate the flows from the proposed development should this be required,
then a connection directly to the watercourse at the south east of the site should be used. It
is worth noting that due to the railway it is required to go through the pedestrian underpass.
Discharge to a Storm Sewer
3.8 As a last resort and if the two previously mentioned options are not feasible a connection to
the sewer will be considered. Any surface water flows that flow through this pipe will need
to be restricted to the Qbar rate of 5l/s via a hydrobrake or similar. Attenuation will then be
required to contain the volume for each rainfall events.
3.9 Discharge to this pipe and then into the DCWW sewer will require their permission.
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4 PROPOSED FOUL WATER DRAINAGE STRATEGY
Proposed Foul Flow
4.1 The proposed development will comprise 40 new residential dwellings. Based upon Sewers
for Adoption 7th Edition, the foul flow has been calculated as 1.85 l/s.
Foul Calculations
4.2 Proposed Foul flow calculations are based on 4000 litres per dwelling per day, which is then
divided by 86400 (24 hours x 60 minutes x 60 seconds) to give a foul flow rate in litres per
second.
Foul Water Drainage Strategy
4.3 A foul only existing network is located within site. DCWW have confirmed connection for foul
only flows to this sewer. Therefore, it is accepted that capacity is available to receive this
amount of foul flow generated by the new development. The proposed development will
utilise a newly built gravity sewer which will discharge to a newly constructed foul pumping
station. This pumping station will then discharge the flows via a newly built rising main to
the connection point given by DCWW in their correspondence.
4.4 Sewers for Adoption 7th Edition confirms that storage for foul pump stations must be
160l/day. Based on this requirement, the pump station requires circa 9.6m3 of storage,
which includes 50% extra storage for emergency purposes should there be a failure of the
pumps.
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5 CONCLUSIONS AND RECOMMENDATIONS
5.1 This report concludes that the proposed development is at no risk of fluvial or tidal flooding.
5.2 Soakaways will be utilised and if this is not proven viable then a watercourse connection and
a sewer connection will be sought in that order.
5.3 Foul water connection to the existing sewer has been granted by DCWW. This will allow for
the pumping station flows to be connected to it at the given location.
5.4 A diversion of the existing sewer will be proposed at detailed design to combine the two foul
and the surface water sewers. This will be done under a S185 agreement.
IMPORTANT SECTION BREAK NEXT – DO NOT DELETE PAST THIS CHEVRON >
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APPENDIX A
APPENDIX B
APPENDIX C