Item5Appendix1bPlans20200077MSC
CAIRNGORMS NATIONAL PARK AUTHORITY Planning Committee Agenda Item 5 Appendix Ib 26/02/2021
AGENDA ITEM 5
APPENDIX ТЬ
2020/0077/MSC
PLANS
BVZRE KAVEL Connection to existing field drain KEY 2380- 239.50 Site Boundary Topographical Survey Contours 0.50m Proposed Finished Contour Proposed Surface Water Sewer Proposed Foul Water Sewer Proposed Septic Tank Proposed Mound Filter System Pipe Proposed Filter Strip Proposed Filter Drain Proposed Filter Trench ACO Channel Proposed Ditch Proposed Reed Bed System Proposed Ditch Alignment OVERHEAD CABLES Recycling B Water Storage 241.53 4No. Feed Bins Sheep Building Area 870m² 4241.00 enuation Basin Bas Level 239.00 Volume 596 m² TOP OF BOTTOM OF BANK SUDS Basin Outlet Headwall 239.000 IL CL 240,500 Flow Croatiel De Spillway Level 240.30 AREA GOBENIEROUS Parking Parking ASS FIELD Bull Pen Building Area 251m³ 241.67 1675 Parking Parking Existing Dry Ditch SW-S3 CL241.526 $1.001 128 SW1 1:34 Area 660m Store and Workshop Equipment, Tractor 1:58.5 225m SW2.000 SW-S2 CL241.391 Straw & Hay Shed Area 375m 1239.00 IL Cattle Building Area 734m² 1 in 37 Channel Catchpit details refer to drawing 50499 – 403 Access Track High Point. Chainage 207.847. Proposed Access Track Irawing 50499 – 501 Klargester Alpha Septic Tank, 3800L Capacity Open Grill Silt Trap naber Note: for reed bed sizing refer to drawing 50499⁄405 Klargester Class 1 Bypass Oil-Water 40 (Inlet) Capacity: 1000 litres Length: 1123mm Diameter: 1225mm C.L 241.50 LL 241.00 (Inlet) L.L 240.90 (Outlet) L at Inlet 240.85 I.L at Outlet 240.35 CF3 240 230.60 Mound Filter POST & WIRE FENCE Distribution Layer (for mound filter system sizing refer to drawing 50499⁄404) BOTTOM OF BANG ‑Mound Basal ‑233 tors 242.0 GRASS Filter material depth between e top of the existing ground and the bottom of the distribution layer should be at east 300mm TOP OF BANK FIELD DRAINAGE DITCH TOP OF BANK POST & WIRE FENCE GRASS GRAVEL TRACK RAILS GRASS POST & WIRE FENCE CONCRETE Outfall to existing field POST POST & GRASS FIELD Outfall to existing field drain GRAVEL TRACK POST & WRE PENCE Outfall to existing field drain Level 235.08 Ditch TOP OF DITCH Existing Ditch GRASS GRASS POST TOM OF BANK TOP OF DENSE POST BOT GRAVEL TRACK BOTTOM OF BA Table 2. SUDs Maintenance Plan POST Component Π Maintenance Schedule Inlet and Outlet Structures Removal of silt and the clearance of grills, gratings of foliage, vegetation, debris and the like and dispose of off site. GRASS GRASS POST & WIRE FENCE Frequency Suggested Personel Every 12 months Farm Operatives SUDs Basin Control Structures/Inspection Chambers Every 12 Farm Operatives 2. Removal of silt and debris and dispose of off site. months Drainage Impact Assessment Notes:
- The surface water drainage system to be discharge to the existing ditch to the south of the site. The network has been designed to accommodate no flooding up to and including the 200year event + 30% Climate Change. Mound Filter Updated, Foul Water Sewer Updated and Feed Drainage Litter Removal Surface Water Drainage Parameters: Table 1. SUDs Pollution Hazard and Mitigation Indices Every 12 Type of Total Total hardstanding area: Treatment Hazard & Mitigation Hydro- Routine collection and removal of litter from the basin and inlet and outlet. Farm Operatives months
- In accordance with the SUDs manual C753, the simple index approach has been utilised to ascertain the total potential pollution hazard. 23.01 For client is Description Contribution Suspended Metals Roofing = 2,954 m² Component Index carbons Grass Cutting As noted Area Solids Farm Operatives The grassed basin is to be cut in April and September. Yard areas 5,933 m² Hazard 0.5 0.4 0.4 Outlet Headwall Structures
- Treatment has been provided as per the mitigation indices from Table 26.3 of the SUDs manual C753. The mitigation provided equals or exceeds the potential pollution index (See Table 1). Ironside Farrar Total = 8,887 m² Roads (low Filter Strip Mitigation Index 1 0.4 0.4 0.5 Manually remove silt, foliage, construction debris, rubbish and the like Every 12 Greenfield run-off (Qbar) = 5.38 I/’s Traffic Roads) Filter Drain Mitigation Index 2 (Note 0.4 0.4 0.5 Farm Operatives and dispose off site in a controlled manner.
- Mitigation treatment is provided through filter Strips, filter drains and a basin for the yard area and roof. Environmental Consultants 111 McDonald Road, EDINBURGH, EH7 4NW 0131 550 6500 | mail@ironsidefarrar. months 6. Attenuation required = 580 m³ Total Mitigation Provided (Note 3) 0.6 0.6 0.75 Attenuation provided: Mitigation treatment is provided through filter strip and filter drain for the access track. EDINBURGH BELLSHILL MANCHESTER Project Name Industrial Hazard 0.3 0.2 0.05 Basin = 611m³ Roofing: Inert Basin Mitigation Index 1 0.5 0.5 0.6 Inspection Chambers Total = 611 m³ > 580 m³ Material Total Mitigation Provided (Note 3) Manually remove silt, foliage, construction debris, rubbish and the like 0.5 0.5 0.6 Every 12 Hazard 0.8 0.8 0.9 Filter Strip Mitigation Index 1 0.4 0.4 0.5 Other Industrial Filter Drain and dispose off site in a controlled manner. Maintain clear of ground cover and scrub vegetation at least 1m offset around the chambers to ensure that they are readily identifiable and accessible. Farm Operatives months Foul Water Drainage Parameters: Filter Drain Mitigation Index 2 (Note 0.4 0.4 0.5 Site Area Basin Mitigation Index 3 (Note 0.5 0.5 0.6 Filter Drain Vegetation Clearance Mound Filter Distribution Layer Area: 63.00m² Total Mitigation Provided (Note 3) 0.85 0.85 >0.95 Maintain clear of ground cover and scrub vegetation at least 1m Every 12 Farm Operatives (A maximum population equivalent of 6 people) 1. Distribution Layer: 6.0m wide and 10.5m long with 5 perforated pipes Septic Tank Sizing 2000 L + (180 x pe) + 2000 + (180 x 6) = 3080 litre Therefore choose 3800 Litre Klargester Alpha Septic Tank or similar approved. Pollution Hazard and Mitigation Indexes Notes: Table 1 shows the total mitigation provided is greater than the Hazard
- In accordance with the SUDS Manual C753 the entire runoff area has been assessed, the SUDS Manual states that where land use varies across the runoff area, the highest pollution hazard within the area shall be used. In this instance the highest pollution hazard is taken as “Other Industrial Site Area”
- A factor of 0.5 is used to account for the reduced performance of secondary or tertiary components associated with already reduced inflow concentrations. offset at either side of the drain to provide a maintenance corridor, and mitigate rootlets penetrating the filer drain geo-textile. Litter Removal months As noted Farm Operatives Routine collection and removal of litter from the filter strip surface. Inspection Surface Inspect filter strip surface to identify evidence of erosion, poor Filter Strip vegetation growth, compaction, ponding, sedimentation and contamination. Inspect silt accumulation rates and stablish appropriate removal frequencies
- Attenuation provided to control the discharge from the development to Greenfield Runoff (QBar) of 5.38 l/s.
- A HR Wallingford Storage estimation assessment of the potential attenuation volume required has been carried out using IH124 Method and the volume required assessed as 580 m³.
- A review of the Water Environment (Controlled Activities) (Scotland) Regulations 2011 demonstrates that this development shall not require SEPA licence to discharge, as the surface water is installed and maintained in accordance with GBR 18, 19, 20 and 21 of the CAR Regulations.
- There are no Scottish Water foul, surface water or combined sewers in the vicinity of the proposal.
- Office facility WC and associated facilities foul drainage to be discharged to septic tank with outfall to drainage field sized in accordance with BS 6297:2007. Client Proposed Drainage Plan & SUDS PPP Condition 2‑M and 2‑N Farm Relocation Balavil Balavil Estate Date 23.01.20 A1 Scale 1:500 Scale Quality Assurance Every 12 months Farm Operatives
- Building roof area water to be collected and discharged directly to the SUDs basin LGB Checked by HR SGS UKAS Certificate GB02/54539 Copyright Acknowledgement Copyright 2019 No. AL100017966 Grass Cutting As noted Farm Operatives Cut grass, manage other vegetation and remove nuisance plants and attenuation provided within the basin to Greenfield Run Off equivalent.
- Farm yard area surface water to be collected in filter strips/filter drains and discharged to the SUDs basin and with attenuation provided within the basin to Greenfield Run Off equivalent. FOR APPROVAL 50499 – 401 P03 Note: Please do not scale from this drawing S2 241.391 1.375 E. 278243.378 N. 802041.448 S3 241.526 2 1.786 E. 278234.949 Ν. 802055.176 240.000 235.000 DATUM 232.000 PROPOSED GROUND LEVEL STORMWATER COVER LEVEL STORMWATER INVERT 241.675 241.675 240.075 Pipe 1.000 Dia 225 STORMWATER DETAILS Circular CLAY 19.072 STORMWATER LENGTHS 241.587 S 35 239.515 241.526 241.500 239.365 MANHOLE SCHEDULE Sheet 1 of 1 241.239 241.172 241.172 241.142 239.150 240.500 240.500 S4 239.150 239.000 24 1.085 Pipe 1.001 Pipe 1.002 Dia 375 Dia 375 Circular CONC 1 in 45 1 in 288 61.923 6.141 239.000 239.000 240.500 S5 239.000 239.039 Basin Pipe 1.003 Dia 375 1 in 11 14.385 237.615 239.000 Outfall 240.000 DATUM 236.000 PROPOSED GROUND LEVEL STORMWATER COVER LEVEL STORMWATER INVERT 241.391 241.391 239.791 Pipe 2.000 Dia 225 STORMWATER DETAILS Circular CLAY 16.109 STORMWATER LENGTHS 241.483 239.515 241.526 Manhole Number Cover Level Pipe Manhole Size Types STORM Network 1 Pipe Diameter Gradient Pipe Upstream Manhole Downstream Manhole Coordinates Depth To Soffit Connections Code Inverts Diams Inv-soff Manhole Cover Code (mm) (1:) Length Number Invert Cover Number Invert Cover 1.000 225 34 19.072 S1 240.08 241.68 S3 239.52 241.53 1.001 375 288 61.923 S3 239.37 241.53 S4 239.15 240.50 S1 241.675 1.375 E. 278225.001 N. 802071.448 1.002 375 156 23.418 S4 239.15 240.50 S5 239.00 240.50 1.003 375 11 15.070 S5 239.00 240.50 S 237.61 239.00 1200 B Unspec 2.000 225 58 16.109 S2 239.79 241.39 S3 239.52 241.53 0 1.000 240.075 225 0 2.000 239.791 225 1 2.000 239.515 225 2 1.000 239.515 225 0 1.001 239.365 375 1 1.001 239.150 375 S4 1 240.500 0.975 E. 278181.595 N. 802023.747 0 1.002 239.150 375 1 1.002 239.000 375 S5 240.500 1.125 E. 278176.124 N. 802000.977 0 1.003 239.000 375 1200 B Unspec 1350 B Unspec 1350 B Unspec Control 1350 Chamber Unspec For client issue Description Ironside Farrar Project Environmental Consultants 111 McDonald Road, EDINBURGH, EH7 4NW 0131 550 6500 | mail@ironsidefarrar. EDINBURGH BELLSHILL MANCHESTER Farm Relocation Balavil Client Balavil Estate Proposed Drainage Longitudinal Sections PPP Condition 2‑M and 2‑N Scale 1:500 Scale 23.01.20 A1 Checked by LG HR Quality Assurance SGS UKAS Certificate GB02/54530 Copyright Acknowledgement Survey Crown Copyright 2019 No. AL100017966 FOR APPROVAL 50499 – 402 P01 Note: Please do not scale from this drawing 75mm BLINDING CONCRETE 500mm MIN 700mm MAX JO FIRST STEP IRON JOINTS/LIFTING EYES SEALED WITH APPROVED BITUMINOUS MATERIAL DUCTILE IRON MANHOLE COVER AND FRAME TYPE D400. MORTAR BEDDING AND HAUNCHING TO COVER AND FRAME TO CLAUSE 4.6.7 675mm min IN ACCORDANCE WITH SCOTTISH WATER POLICY 1 TO 3 COURSES OF 215mm THICK CLASS B ENGINEERING BRICK TYPE 1 OR TYPE 2 CONCRETE COVER SLAB BEDDED ON MORTAR. SHAFT DIAMETER AS NOTED IN MANHOLE SCHEDULE AND IN ACCORDANCE WITH SCOTTISH WATER POLICY TOP AND BOTTOM RINGS TO BE PLAIN ENDED. GRANOLITHIC CONCRETE TOPPING TO BE BROUGHT UP TO A DENSE SMOOTH FACE NEATLY SHAPED AND FINISHED TO ALL BRANCH CONNECTIONS (MIN THICKNESS 50mm) 300mm ‑MANHOLE RUNGS PRECAST CONCRETE MANHOLE SECTIONS AND COVER SLAB TO BE BEDDED WITH MORTAR, PLASTOMERIC OR ELASTOMERIC SEAL CONFIRMING TO BS EN 1917 AND BS 5911 – 3 100 min CONSTRUCTION JOINT SELF-CLEANING TOE HOLES O BE PROVIDED WHERE CHANNEL EXCEEDS 600mm WIDE INVERTS TO BE FORMED USING CHANNEL PIPES IINTEGRAL IN-SITU ST4 CONCRETE BASE WALLS BENCHING & BASE SLAB WITH PRECAST CHANNEL AS SHOWN OR IN-SITU FORMED INVERT AS ALTERNATIVE. WALLS TO EXTEND 50 BEYOND OUTER FACES OF CHAMBER RING. ALTERNATIVLEY PRECAST CONCRETE CHAMBER RINGS MAY BE BEDDED IN MORTAR ON AN IN-SITU ST4 CONCRETE BASE SLAB 300 GREATER IN DIAMETER THAN INTERNAL DIAMETER OF CHAMBER RINGS. ALL CONCRETE MUST USE SULPHATE RESISTANT CEMENT. DETAIL 1 BARREL OF PIPE, 200mm TO PC CONCRETE MANHOLE TYPE B DEPTH UP TO 3.0m (1:20) ‑THE BOTTOM PRECAST MANHOLE RING TO BE BUILT INTO BASE CONCRETE MINIMUM 75mm 150 x 150 mm GRADE ST4 VORTEX FLOW CONTROL AS PER MICRODRAINAGE CALCULATIONS TO BE INSTALLED AT OUTLET PIPE. 1002 3750 mm DIA PIPE INLET PIPE 3750 mm DIA PIPE OUTLET PIPE 1.003 DETAIL 2 CONTROL MANHOLE 2400mm INTERNAL DIA. 675mm x 675mm SQUARE ACCESS POINTS (STEP IRONS OMITTED FOR CLARITY) WITH CLASS D400 COVERS CONTROL CHAMBER MHS6 — PLAN (1:50) CENTRAL WEIR 200mm THICK TO BE KEYED INTO P.C.C. UNITS. 10mm DOWELS AT 300mm CENTRES TO BE PROVIDED TO TIE INTO REINFORCING MESH IN WEIR WALL & KEYED INTO THE BASE WITH 10mm DOWELS AT 300mm CENTRES BENCHING SLOPE ΤΟ ΒΕ 1:10 ΤΟ 1:30 75mm BLINDING CONCRETE 3750 mm OUTLET PIPE 239.000mg 250mm THICK COMPACTED GRANULAR MATERIAL. 240.500m DOUBLE ENCAPSULATED STEP RUNG 239.953 PENSTOCK VALVE/DRAIN DOWN 239.00m0 500mm 3750 mm Base Level INLET PIPE 150mm MIN. MASS CONCRETE SURROUND TO PIPEWORK. GRADE ST4 CONCRETE 75mm THICK. QUALITY CONTROL THROTTLE, HYDROBRAKE FLOW CONTROL DEVICE. 5.381/s DISCHARGE, 1.2m HEAD CONTROL MANHOLE MHS6 SECTION (1:50) Notes:
- Refer to “Sewers for Scotland, 4th Edition” for typical details of manholes with depths from cover level to soffit of pipe not exceeding 6m. No significant departure from these shall be made without the approval of Highland Council. Types D&F need the agreement of Scottish Water. Manholes should be designed and constructed in accordance with BS EN 752 – 3.
- Manhole diameter to be as follows: 1200mmØ (Pipe Ø up to 375mm.) 1500mmØ (Pipe Ø > 375mm up to 700mm.) 1800mmØ (Pipe Ø > 750mm up to 900mm.)
- Manhole construction to be in accordance with “Sewers for Scotland, Fourth Edition”, (SFS4).
- Manhole covers and frames to be in accordance with SFS4 sub-section 5.2.30.
- Rocker pipes shall be provided at entry to and exits from manholes. Their length shall be as shown in the Table in sub-section 5.6.6 of SFS4.
- Where step rungs and ladders are to be used top-step rungs are to be located not less than 500mm and not greater than 700mm from the finished manhole cover level with a minimum of two courses of brickwork.
- Chambers more than 450mm in depth have to have one or more step rungs or toe holes and 25mm diameter solid bar handrail to be provided to the benching.
- Where no step rungs are to be used, there shall be between two and four courses of brickwork under cover.
- Refer to SFS4 sub-section 2.20.7 for minimum clear access opening sizes and requirements for fittings.
- Pipes of different diameters entering manholes shall be installed with soffits at the same level.
- Clause numbers to the Specification for Highway Works (S.H.W.)
- Pipe materials shall be in accordance with part 4 Sewers for Scotland 4th Edition.
- The use of perfect manhole or similar precast base units shall be precluded without the express consent of the engineer. OUTLET 200mm 500mm MIN 700mm MAX TO FIRST STEP IRON 300mm DUCTILE IRON MANHOLE COVER AND FRAME TYPE D400. 675mm DESIGNATION (1) MORTAR BED TO GRATING & FRAME (10 MIN 20 MAX) TO ‑SHW SERIES 2400 BRICKWORK TO SHW SERIES 2400 OR PRECAST CONCRETE ADJUSTING UNIT TO BS EN 1917 AND BS 5911 – 3 150mm THICK SPECIAL SEATING SLAB TO BE USED WITH TYPE1 & TYPE 2 COVER SLABS. MANHOLE RUNGS DIAMETER AS NOTED IN MANHOLE SCHEDULE CAPPED PIPE END TOP AND BOTTOM RINGS TO BE PLAIN ENDED. PRECAST COVER SLAB BEDDED ON 10 MIN BED DESIGNATION (i) TO SHW SERIES 2400 INLET PRECAST CONCRETE CHAMBER RINGS. CAPPED PIPE END 50mm 300mm 150mp DETAIL 3 FILTER TRENCH CATCHPIT DETAIL SCALE (1:20) INLET ‑JOINTS SEALED WITH APPROVED TROWELLING GRADE BITUMINOUS MATERIAL OR PREFORMED JOINTING STRIP AS PER MANUFACTURERS INSTRUCTIONS. 150 x 150 mm GRADE ST4 PRECAST CONCRETE RINGS BEDDED ON CEMENT MORTAR. IN-SITU ST4 CONCRETE BASE SLAB DEPTH VARIES 600mm 150mm TOPSOIL ‑FINISH BACKFILL TO TRENCH IN ACCORDANCE WITH S.H.W. CLAUSE 505.2 DETAIL 4 FILTER DRAIN SCALE (1:20) TYPE B MATERIAL TO S.H.W CLAUSE 503.3 (ii) TERRAM 700 MEMBRANE 150mm POROUS PIPE PERFORATIONS LAID UP TYPE A MATERIAL TO S.H.W CLAUSE 503.3 (1) DEPTH VARIES 600mm 150mm TOPSOIL FINISH BACKFILL TO TRENCH IN ACCORDANCE WITH S.H.W. CLAUSE 505.2 TYPE B MATERIAL TO S.H.W CLAUSE 503.3 (ii) TERRAM 700 MEMBRANE DETAIL 5 EMBANKMENT FILTER TRENCH SCALE (1:20) TYPE A MATERIAL TO S.H.W CLAUSE 503.3 (i) 2 No. 50mmØ Perforated Pipes with filter material surround (single sized granular material, 14mm no Limestone) 600mm DETAIL 6 MAIN “LOW FLOW” CHANNEL SCALE 1:10 For client issue Description Ironside Farrar Project Environmental Consultants 111 McDonald Road, EDINBURGH, EH7 4NW 0131 550 6500 | mail@ironsidefarrar. EDINBURGH BELLSHILL MANCHESTER Farm Relocation Balavil Client Balavil Estate Proposed Drainage Drainage Details PPP Condition 2‑M and 2‑N Scale 1:500 Scale Date 23.01.20 A1 LG Checked by HR Quality Assurance SGS UKAS Certificate GB02/54539 Copyright Acknowledgement FOR APPROVAL 50499 – 403 Crown Copyright 2019 No. AL100017966 P01 Note: Please do not scale from this drawing Mound Filter System Calculations to BRE Digest No. 478, Mound Filter Systems for the Treatment of Domestic Wastewater Vp from percolations text results = 186.9 Minimum Basal Area Resultant Mound Dimension The resultant dimension meet the critical dimension for distribution layers bed as per BRE 478 — Fig 14 and Figure. At = P x Vp x 0.25 A = Distribution layer width B = P = Distribution layer length 6.00 m C = Downslope taper 10.50 m Vp = At = Percolation value of the native soil (s/mm) 6 D = Area 186.9 E = Depth of filter material at the upslope edge 9.61 m 280.3 m² F = Minimum Distribution Layer Area G = Depth of gravel in the distribution layer Depth of filter material at the downslope edge 0.33 m 1.14 m H = Depth of the cover at the upslope and downslope 0.20 m Ad = P x Vf x 0.25 J = Upslope taper Depth of cover at the centre of the distribution layer 0.30 m 1.40 m P = K = Population Equivalent Sideslope taper 1.50 m Vf = Ad = Distribution layer area (m²) Percolation value of filter material (s/mm) 6 L = 35 W = Total length of mound [B+2K] 5.75 m 52.5 m² X = Total Width of the Mound [A+C+J] 21.90 m Length of Pipework within Distribution Layer Total height of mound H+J+[(D+E)/2] 17.11 m 2.34 m Ad = Ad = Pipes = Adopt 5 pipes Length = Length of each pipe Distribution Layer Area At = 52.5 Mound Basal Area (L X w) 63.0 m² X = Height 371.5 m² 5 2.3 m² 241.00 10.5 m Assuming 6.0m distribution layer width. Therefore Width between pipes 1.2 m Therefore distribution layer area = 10.5 m x 6.0m = 63.00 m² 240.50 240.00 + 239.50 ‑K-5.7m- 239.00 238.50 238.00 Backfill with selected excavated material free from large objects 100mmØ Perforated pipe Permeable Geotextile H= 1.4m G= 0.65m D= 0.33m 240.000 A= 6m F=0.2m 1.2m E=1.14m J= 1.5m DATUM 235.000 Existing Ground Level Proposed Level Distribution Layer Vf = 35s/mm Percolation Rate 4.000 6.000 8.000 C= 9.61m W= 17.11m Mound Filter Cross Section A‑A’ Scale H 1:50 V 1:50 239.178 237.680 12.000 Proposed Finish Level 238.398 237.410 14.000 Usable Fill 5 – 30 min / 25mm Percolation Rate 3 1 237.622 237.131 16.000 236.845 236.787 18.000 236.741 236.741 18.269 237.50 237.00 KEY ‑240.0 1 in 3 3 2397 CL 240.50 L 239.50 ‑K-5.7m- + ‑239.0- Distribution Layer ‑237.0 238.58 Mound Basal Mound Filter System Plan Scale 1:100 For client issue Description Ironside Farrar Environmental Consultants 111 McDonald Road, EDINBURGH, EH7 4NW 0131 550 6500 | mail@ironsidefarrar. EDINBURGH BELLSHILL MANCHESTER Project Name Farm Relocation Balavil Client Balavil Estate Title Proposed Mound Filter System Notes Proposed Filter Strip
- The area required for the mound shall be fenced to avoid traffic and constructions. This will prevent disturbance, scalping or Proposed Filter Drain compaction of the mound.
- The septic and infiltration system shall be inspected annually. Proposed Reed Bed System Date PPP Condition 2‑M and 2‑N Scale 1:500 Scale 07.05.20 A1 LG Checked by HR Quality Assurance SGS UKAS Certificate GB02/54530 Copyright Acknowledgement FOR APPROVAL 50499 – 404 Crown Copyright 2019 No. AL100017966 P02 ‑238.0- 237.44 Note: Please do not scale from this drawing Wash Bay Reed Bed Sizing Calculations Sizing based on the Recommendations from BRE Publication ‘Reed Beds for the Treatment of Domestic Wastewater’ Recommended size of reed bed = 5m²/PE Calculation of Flow Pressure washer with a flow rate of 10 litres per minute. Assume 5 minutes per wash Therefore flow = 10 x 5 = 50 litres per wash Hose with a flow rate of 20 litre per minute Assume 5 minutes per wash Therefore flow = 20 x 5 = 100 litre per wash Therefore size for hose wash Assume 3 Wash per day Therefore flow per day = 3 x 100 = 300 litre per day Calculation of Population Equivalent Flow for one person = 180 litre per day Therefore PE equivalent = 300⁄180 = 1.7 = 2 Persons Sizing of Reed Bed Recommendation Size = 5m² / PE Therefore minimum reed bed area = 5 x 2 = 10m² Recommended length to width ratio for a reed bed 4:1 for PE ≤ 30