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HomeMy WebLinkAbout2624 - Site Assessment ReportAPPENDIX A: SITE CHARACTERISATION FORM File Reference: Prefix: First Name: Chloe Cassidy Surname: Denis Ward Address: Site Location and Townland: Carrickartagh, Carrickmacross, Co. Monaghan Number of Bedrooms: [3 Comments on population equivalent Maximum Number of Residents: 5 Proposed Water Supply: Mains Private Well/Borehole W] To be bored on -site I Group Well/Borehole Soil Type, (Specify Type): Subsoil, (Specify Type): Acid Brown Earths, Brown Podzolics Sandstone and shale till (Lower Paleozoic) Bedrock Type: Silurian Metasediments and Volcanics Aquifer Category: Regionally Important Locally Important Poor PI Vulnerability: Extreme High [✓ Moderate Low Groundwater Body: Status �J Name of Public/Group Scheme Water Supply within 1 km: Source Protection Area: ZOC SI SO Groundwater Protection Response: I— R1 Presence of Significant Sites (Archaeological, Natural & Historical): None fl �� 3 / Past experience in the area: None Comments: I (Integrate the information above in order to comment on: the potential suitability of the site, potential targets at risk, and/or any potential site restrictions). Following the desk study the site appears suitable for the safe disposal of effluent subject to GPR of R1 which states Acceptable subject to normal good practice. Where domestic water supplies are located Nearby, particular attention should be given to the depth of subsoil over bedrock such that the minimum depths required in Chapter 6 are met and the likelihood of microbial pollution is minimised Note: Only information available at the desk study stage should be used in this section. 3.1 Visual Assessment Landscape Position: Undulating Hills Slope: Steep (>1:5) U Shallow (1:5-1:20) U Relatively Flat (<1:20) U Slope Comment Sloping north to south Sloping north to south Sloping north to south Surface Features within a minimum of 250m (Distance To Features Should Be Noted In Metres) Houses: Derelict cottage to north. No other houses within >200m House >200m to south Existing Land Use: Agriculture Vegetation Indicators: Grass Groundwater Flow Direction: North to south Ground Condition: Firm Underfoot Site Boundaries: Trees, Hedgerows and Stone Walls 3.1 Visual Assessment (contd.) Roads: Access lane to west. Cul de sac to south. Outcrops (Bedrock And/Or Subsoil): None Visible Surface Water Ponding: None Visible Lakes: None Visible Beaches/Shellfish Areas: None Visible Wetlands: None Visible Karst Features: None Visible Watercourses/Streams:* None Visible *Note and record water level 3.1 Visual Assessment (contd.) Drainage Ditches:* None Visible Springs:* None Visible Wells:* Adjoining houses served by group scheme. No wells within 70m of proposed percolation area. Comments: (Integrate the information above in order to comment on: the potential suitability of the site, potential targets at risk, the suitability of the site to treat the wastewater and the location of the proposed system within the site). Following the visual assessment the site appears suitable for the safe disposal of effluent. *Note and record water level 3.2 Trial Hole (should be a minimum of 2.1m deep (3m for regionally important aquifers)) To avoid any accidental damage, a trial hole assessment or percolation tests should not be undertaken in areas which are at or adjacent to significant sites, (e.g. NHAs, SACs, SPAs, and/or Archaeological etc.), without prior advice from National Parks and Wildlife Service or the Heritage Service. Depth of trial hole (m): 3.0 Depth from ground surface Depth from ground surface to bedrock (m) (if present): to water table (m) (if present): 2.5 Depth of water ingress: L_ Rock type (if present): Date and time of excavation: 01 -Mar -2026 L 18:20 Date and time of examination: 04 -Mar -2026 07:20 Depth of Surface and Subsurface Soil/Subsoil Percolation Texture & Plasticity and Soil Density/ Colour**"* Preferential Tests Classification** dilatancy*** Structure Compactness flowpaths 0.1 m 0.2 m 0.3 m 0.4 m 0.5 m 0.6 m 0.7 m 0.8 m 0.9 m 1.0 m 1.1 m 1.2 m 1.3 m 1.4 m 1.5 m 1.6 m 1.7 m 1.8 m 1.9 m 2.0 m 2.1 m 2.2 m 2.3 m 2.4 m 2.5 m 2.6 m 2.7 m 2.8 m 2.9 m 3.0 m 3.1 m 3.2 m 3.3 m 3.4 m 3.5 m TOPSOIL GRAVELLY CLAY GRAVEL BOULDERS GRAVELLY CLAY GRAVEL BOULDERS WATER LEVEL 2.5M BELOW G.L. Dfoc 'Jr I RII%L HOLE 3.0M 2-3 THREADS CRUMB FIRM <100mm RIBBONS DILATANT 4 THREADS STRUCTURE- FIRM Likely Subsurface Percolation Value: 50 Likely Surface Percolation Value: 20 FIRM BROWN NONE ROOT ZONE LIGHT NONE BROWN/ GREY PATCHES BROWN IVIV I I LOYV !- 1.5M Note: 'Depth of percolation test holes should be indicated on log above. ('Enter Surface or Subsurface at depths as appropriate). " See Appendix E for BS 5930 classification. "3 samples to be tested for each horizon and results should be entered above for each horizon. "" All signs of mottling should be recorded. NONE 3.2 Trial Hole (contd.) Evaluation: Following the trail hole inspection the site appears suitable for the safe disposal of effluent. 3.3(a) Subsurface Percolation Test for Subsoil Step 1: Test Hole Preparation Percolation Test Hole 1 2 3 Depth from ground surface 900 900 900 to top of hole (mm) (A) Depth from ground surface I 1,340 1,350 1,3501 to base of hole (mm) (B) Depth of hole (mm) [B - A] 1 440 450 450 Dimensions of hole 340 x 320 360 x 31011 310 x 350 [length x breadth (mm)]II Step 2: Pre -Soaking Test Holes Pre-soak start Date 03 -Mar -2026 03 -Mar -2026 03 -Mar -2026 Time 09:20 09:20 09:20 2nd pre-soak Date 03 -Mar -2026 03 -Mar -2026 03 -Mar -2026 start Time 17:25 17:25 17:25 Each hole should be pre-soaked twice before the test is carried out. Step 3: Measuring T100 Percolation Test Hole No. 1 2 3 Date of test I 04-03-2026 j 04-03-2026 04-03-2026 Time filled to 400 mm � 07:31 07:33 07:36 Time water level at 300 mm I 10:10 10:15 10:07 Time (min.) to drop 100 mm (T100) I 159.00 162.0011151.00 Average T100 I 157.33 If T100 > 480 minutes then Subsurface Percolation value >120 — site unsuitable for discharge to ground If T100 < 210 minutes then go to Step 4; If T100 > 210 minutes then go to Step 5; Step 4: Standard Method (where T100 < 210 minutes) Percolation Test Hole 1 2 3 Fill no. Start Finish At (min) Start Finish At (min) Start Finish At (min) Time Time Time Time Time Time (at 300 (at 200 (at 300 (at 200 (at 300 (at 200 mm) mm) mm) mm) mm) mm) 1 10:10 13:12M 182.00 I 10:15 13:251L190.00 10:07 12:5711 170.00 2 13:12 16:4011 208.00 13:25 16:5711 212.00 12:57 16:1911 202.00 3 16:40 20:3711 237.00 16:57 21:0111 244.00 16:19 20:1211 233.00 Average At 209.00 215.33 201.67 Value Average At/4 = Average At/4 = Average At/4 = [Hole No.1] I 52.251(t1) [Hole No.2] I 53.831(t2) [Hole No.3] 50.421(t3) Result of Test: Subsurface Percolation Value = 1 52.171 (min/25 mm) Comments: -VALUE WITHIN THE ALLOWABLE RANGE SET OUT IN THE EPA GUIDELINES Step 5: Modified Method (where Ti., > 210 minutes) Percolation Test Hole No. Percolation Test Hole No. 2 Fall of water Time Start Finish Time K,s T- Fall of water Time Start Finish Time K,s T — in hole (mm) Factor Time Time of fall = T, Value in hole (mm) Factor Time Time of fall = Tf Value =T hh:mm hh:mm (mins) IT,, =4.45 =T1 hh:mm hh:mm (mins) / Tm =445 =Tm /Ks =Tm /Ks 300-250 I 8.1 0 0.00 I 300-250 8.1 0.0011I 250-200 9.7 0 0.00 � 250-200 9.7 00 0.00 �� 200 -150 11.9 OLD 0.0011� 200 - 150 11.9 0� 0.00 �� 150-100 14.1 � 0.0011� 150- 100 14.1 �� 0.00 �� Average T- Value T- Value I -tole 1 = (Ti) I 0.001 Average T- Value T- Value Hole 2 = (T2) I 0.00 Percolation Test Hole No. 3 Fall of water Time Start Finish Time K,, T — in hole (mm) Factor Time Tim§e of fall = T, Value = T, hh:mm hh:mm (mins) / Tm = 4.45 =T /i43 300 - 250 8.1 0.00 l I 250 -200 9.7 0.00 I� 200-150 11.9 �� 0.00 �� 150-100 14.1 � 0.0011� Average T- Value T- Value Hole 3 = (12) 0.00 Result of Test: Subsurface Percolation Value = 0.00 (min/25 mm) Comments: 3.3(b) Surface Percolation Test for Soil Step 1: Test Hole Preparation Percolation Test Hole Depth from ground surface to top of hole (mm) Depth from ground surface to base of hole (mm) Depth of hole (mm) Dimensions of hole [length x breadth (mm)] Step 2: Pre -Soaking Test Holes 1 2 3 0 0 0 450 460 440 450 460 440 300 x 340 340 x 340 350 x 350 Pre-soak start Date I 03 -Mar -2026 03 -Mar -2026] 03 -Mar -2026 Time I 09:20 09:20 09:20 2nd pre-soak Date 03 -Mar -2026 03 -Mar -2026 I L 03 -Mar -2026 start Time 17:25 I 17:25 17:25 Each hole should be pre-soaked twice before the test is carried out. Step 3: Measuring T100 1 2 3 Percolation Test Hole No. Date of test 04 -Mar -26 II 04 -Mar -26 04 -Mar -2026 Time filled to 400 mm 07:40 07:42 07:42 Time water level at 300 mm F_ 08:25 F 08:20 F 08:30 Time to drop 100 mm (Ti®) 45.00 II 38.00 II 48.00 Average T100 43.67 If T100 > 480 minutes then Surface Percolation value >90 - site unsuitable for discharge to ground If T1oo ≤ 210 minutes then go to Step 4; If T100 > 210 minutes then go to Step 5; Step 4: Standard Method (where T100 ≤ 210 minutes) Percolation Test Hole 1 2 3 Fill no. Start Finish AT (min) Start Finish AT (min) Start Finish AT (min) Time Time Time Time Time Time (at 300 (at 200 (at 300 (at 200 (at 300 (at 200 mm) mm) mm) mm) mm) mm) 1 08:25 09:21M56.00 08:201109:09 49.00 08:301109:2811 58.001 2 09:21 10:3511 74.00 09:09 10:051P 56.00 09:28 10:4811 80.00 3 10:35 12:1111 96.00 10:05 11:1711 72.00 10:481112:2311 95.00 Average AT 75.33 59.00 77.67 Value Average AT/4 = Average AT/4 = Average AT/4 = [Hole No.1] 18.831(T1) [Hole No.2] I 14.751(T2) [Hole No.3] 19.42 (T3; Result of Test: Surface Percolation Value = 17.67 (min/25 mm) Comments: P -VALUE WITHIN THE ALLOWABLE RANGE SET OUT IN THE EPA GUIDELINES Step 5: Modified Method (where T100 > 210 minutes) Percolation Test Hole No. Fall of water Time Start Finish Time K„ T — in hole (mm) Factor Time Time of fall = T, Value = Tf hh:mm hh:mm (mins) / Tm = 4.45 =Tm /K1 300 - 250 8.1 0.00 �� 250 - 200 9.7 0 0.00 �� 200 -150 11.9 00 0.0011� 150-100 14.1 0� 0.0011� Average T- Value T- Value Hole 1 = (Ti) 0.00 Percolation Test Hole No. 3 Fall of water Time Start Finish Time Kf, T — in hole (mm) Factor Time Time of fall =Tf Value =Tf hh:mm hh:mm (mins) ITm =4.45 = Tm /K 300 -250 8.1 0.00 �� 250 -200 9.7 �0 0.00 �� 200 -150 11.9 OLD 0.00 �� 150-100 14.1 �� 0.0011� Percolation Test Hole No. 2 Fall of water Time Start Finish Time K T - in hole (mm) Factor Time Time of fall = T, Value = Tf hh:mm hh:mm (mins) / Tm = 4.45 = Tm / KIB 300 - 250 I 8.1 0.00 00 250 - 200 9.7 00 0,00 �� 200-150 11.9 �� 0.00 � 150-100 14.1 �� 0.00 ____ _____ Average I T- Value T- Value Hole 2 = (T2) I 0.00 Result of Test: Surface Percolation Value = 0.00 (min/25 mm) Comments: Average I T- Value T- Value Hole 3 = (T2) I 0.00 L.___________________________________________ Integrate the information from the desk study and on -site assessment (i.e. visual assessment, trial hole and percolation tests) above and conclude the type of system(s) that is (are) appropriate. This information is also used to choose the optimum final disposal route of the treated wastewater. Slope of proposed infiltration / treatment area: o Are all minimum separation distances met? I // Depth of unsaturated soil and/or subsoil beneath invert of gravel (or drip tubing in the case of drip dispersal system) 0.90 Percolation test result: Surface: L 52.17 Not Suitable for Development I Identify all suitable options Septic tank system (septic tank and percolation area) (Chapter 7) No 2. Secondary Treatment System (Chapters 8 and 9) and soil polishing filter Yes (Section 10.1) 3. Tertiary Treatment System and Infiltration / treatment area (Section 10.2) Yes Sub -surface: 17.67 Suitable for Development Discharge Route' GROUNDWATER Propose to install: Secondary Treatment System and soil polishing filter and discharge to: Ground Water Invert level of the trench/bed gravel or drip tubing (m) 0.60 Site Specific Conditions (e.g. special works, site improvement works testing etc. Due to the mottling level at 1.5m blelow G.L., it is proposed to install an effluent treatment system and carry out site improvement works. Soil polishing filter to be constructed to ensure that there is a minimum of 0.9m of suitable percolating material between the base of the lowest part of the percolation area/soil polishing filter and winter groundwater level/bedrock at all times. The distribution pipes used in this system are smooth walled, have a diameter of 38mm, with 7mm holes drilled in them 300mm apart, and each pipe was spaced parallel and 600mm apart. The distribution pipes to be bedded on 250mm depth of washed pebble (20 - 30 mm in size). Once the distribution pipes are in place they are to be surrounded and covered to a depth of 150mm of washed pebble which should extend the full width of the soil polishing filter. Before the distribution pipes to be backfilled with the topsoil the crushed stone is covered with geotextile or similar permeable materials. (this is to prevent the stone being silted up with topsoil. ) See documents attached for sizing and construction details. All works to be carried out as per the Manufacturers instructions, epa guidelines, building regulations and drawings attached with this report. All separating distances to be achieved and all works to be carried out in accordance with current EPA guidelines ' A discharge of sewage effluent to "waters" (definition includes any or any part of any river, stream, lake, canal, reservoir, aquifer, pond, watercourse or other inland waters, whether natural or artificial) will require a licence under the Water Pollution Acts 1977-90. Refer to Section 2.4. SYSTEM TYPE: Septic Tank Systems (Chapter 7) Tank Capacity (m3) Percolation Area No. of Trenches Length of Trenches (m) 0 Invert Level (m) 0 Mounded Percolation Area No. of Trenches Length of Trenches (m) 0 Invert Level (m) 0 SYSTEM TYPE: Secondary Treatment System (Chapters 8 and 9) and polishing filter (Section 10.1) Secondary Treatment Systems receiving septic tank effluent (Chapter 8) Media Type Area (m2)* Depth of Filter Invert Level Sand/Soil Soil Constructed Wetland Other Polishing Filter*: (Section 10.1) Surface Area (m2)* Option 1 - Direct Discharge Surface area (m2) Option 2 - Pumped Discharge Surface area (m2) Packaged Secondary Treatment Systems receiving raw wastewater (Chapter 9) Type SEE MANUFACTURERS REPOR Capacity PE 6 Sizing of Primary Compartment 3.00 m3 Option 3 - Gravity Discharge Trench length (m) 250.00 Option 4 - Low Pressure Pipe Distribution 0 Trench length (m) Option 5 - Drip Dispersal Surface area (m2) SYSTEM TYPE: Tertiary Treatment System and infiltration / treatment area (Section 10.2) Identify purpose of tertiary Provide performance information Provide design information treatment demonstrating system will provide required treatment levels MOTTLING LEVEL 1.5M BELOW G.L. DISCHARGE ROUTE: SEE MANUFACTURERS REPORT SEE MANUFACTURERS REPORT Groundwater ❑✓ Hydraulic Loading Rate * (I/m2.d) 3.00 Surface area (m2) 250.00 Surface Water ** ❑ Discharge Rate (m3/hr) * Hydraulic loading rate is determined by the percolation rate of subsoil ** Water Pollution Act discharge licence required QUALITY ASSURANCE: Installation & Commissioning SEE MANUFACTURERS REPORT On -going Maintenance SEE MANUFACTURERS REPORT Company: rARC Design Services Prefix: Mr First Name: Oliver Surname: Farrelly Address: Viountain Pole, <ells, moo. Meath. Qualifications/Experience: IFETAC Cert Attached Date of Report: I 23 -Mar -2026 Phone: I 0879520269 E-mail I arcdesignservices@gmail.com Indemnity Insurance Number: See Insurance Cert Attached Digitally signed by Oliver Farrelly Oliver Farrell y Date: 2026.03.23 17:07:48 Z Signature: IyF Location of Test Holes +•��,�Yy +, tt y .4.- 1 -Test Hole 1 r I,. 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GSI Bedrock Aquifer PI 651 Rock Unit Groups Silurian Metaseditnents and Volcanics GSI Vulnerability High Vulnerability National Soils AminDW IFS_Soil AminDW Parent_Material TLPSsS IFS_Description Acid Deep Well Drained t..lireral Drained iaineral IFS_Type Deep well drained mineral - Derived from mainly non calcareous parent materials Soil_Group Acid Brown Earths, Brown Podzotics County MONAGHAN IFS_Code 11 Subsoils 3811391.49781 M b PERIMETER 3811391.49781 PAR MAT TLPSsS COUNTY MONAGHAN CATEGORY Till type DESCRIPT Sandstone and shale tilt (Lower Paleozoic) TEXTURE Clayey Class Tills(diamictons) PlalnEnglish Thesubswl is a tilt type. Till Is sediment deposited by or from glacier ice. rr` radius Insurance Solutions Insurance Cover Note 2025 Insured Oliver Farrelly T/A Arc Design Services Address Mountainpole, Kells, Meath, Business Description Ecology Consultancy Cover Details Professional Indemnity €1,000,000 Insurer OPTIS Insurances Ltd T/A Optis Insurance Policy Number BS0545-PI-151 Inception Date 08/12/2025 Renewal Date 08/12/2026 3rd Floor, Block 1 Quayside Business Park Mill Street, Dundalk, Co. Louth Ireland 042 939 3993 w,.%iv-radiusinsurance solutions. cowrie �� ETAC �.. Further Education and ®_ rrninrneawardt councd ® Cnml Mi m nQdnd�och[o'N H, vo 1whn clue O:tiivio National Skills Certificate (FAS) Awarded to Bronnta er Oliver Farrelly who has achieved the National Standards for a bhain Caighde6in Ndisiunto omach maidir le Site Suitability Assessment for On -Site Wastewater Treatment Systems 1` ® '_#'2 �/t- i Chan, FETAC Ch,(E ewzh . FErAC F/NSC 003488