Loading...
HomeMy WebLinkAboutSW6220505_Soils/Geotechnical Report_20220607Scott Cole, NCLSS 312 Copples Road Ext Asheboro, NC 27205 (336) 460-4554 Double D Engineering, PLLC Attn: Mr. Lee Humphrey 150 S. Page Street Southern Pines, NC 28387 March 21, 2022 Re: Seasonal High -Water Table Identification and Soil Infiltration Rates: Rockfish Road site, Raeford, NC; Hoke County NC parcel 494750301009. Soil conditions and infiltration rates were evaluated and measured on the above -referenced property within the proposed storm water BMP device. Work was conducted in accordance with Parts A-2 and C-1 of the North Carolina Department of Environmental Quality Stormwater Design Manual. Soil samples were evaluated with a hand auger. SEASONAL HIGH WATER TABLE IDENTIFICATION Seasonal High Water Table depth is determined by field evaluation for soil wetness conditions which are indicated by the presence of redoximorphic (rdox) features with chroma colors of 2 or less (in Munsell color notation) in mottles or the horizon matrix, and at times, saturated soil conditions and/or free water within the soil profile. Colors of chroma 2 or less due to relic minerals from parent material (underlying rock), anaerobic activity created by placement of fill material, or soil textural class transitions (perched water) are not considered as indicators for seasonal high water. Upon determination of SHWT depth, an additional 6" will be deducted from the observed depth to account for capillary fringe water movement above the SHWT. Stormwater infiltration trenches are designed to ensure the lowest point is at least two feet above the Seasonal High Water Table (SHWT). SATURATED HYDRAULIC CONDUCTIVITY Mgt) Soils evaluated on this property are typical of those within the Johnston and Blaney Soil series. These soils are moderately well drained soils with varying rates of permeability. Infiltration rates are measured to determine if soil conditions are suitable for the installation of stormwater infiltration devices. Infiltration rates are measured using a Johnson Constant Head Permeameter. Measurements are recorded at varying intervals until equilibrium was reached. The SHWT and Infiltration rates for the stormwater BMP devices are reported for each proposed location in the tables below. BMP Device Site #1 Test Location SHWT Munsell Color Ksat #1 Ksat #2 Ksat #3 (feet below Notation round surface 11' bgs 5Y 8/1 0-18" 18-50" 5011+ BMP Site 1 2.5Y 7/1 Sandy Loam Sandy Clay Exp. Elevation 205' 8" / hour Loam (heavy) Clay/Heavy 2.5" / hour Redox Not Measured Scott Cole, NCLSS 312 Copples Road Ext Asheboro, NC 27205 (336) 460-4554 BMP Device Site #2 Test Location SHWT Munsell Color Ksat #1 Ksat #2 Ksat #3 (feet below Notation round surface 10' bgs 5Y 8/1 0-24" 24-50" 5019+ BMP Site 2 2.5Y 7/1 Sandy Loam Silty Clay Exp. Elevation 189' 8" / hour 2.5" / hour Clay/Heavy Redox Not Measured BMP Device Site #3 Test Location SHWT Munsell Color Ksat #1 Ksat 92 Ksat #3 (feet below Notation round surface 9' bgs 5Y 8/1 0-36" 3659+ N/A BMP Site 3 2.5Y 7/1 Sandy Loam Exp. Elevation 184' 8" / hour Clay/Heavy Redox Not Measured BMP Device Site #4 Test Location SHWT Munsell Color Ksat #1 Ksat #2 Ksat #3 (feet below Notation round surface 9' bgs 5Y 8/1 0-24" 24-48" 4811+ BMP Site 4 2.5Y 7/1 Sandy Clay Sandy Clay Exp. Elevation 197' Loam 0.2" / hour Clay/Heavy 2.5" / hour Redox Not Measured CONCLUSION Field evaluation of hydraulic conductivity provides estimations of soil infiltration rates; however, methods used to measure these rates can influence the results. Side walls of the bore hole are "smeared" by the soil auger as the hole is prepared and loose soil in the bottom of the hole is placed in suspension when water is applied; both of these factors negatively influence water infiltration rates. To help overcome these issues, after excavation of each infiltration trench, it is recommended the trench bottom and sidewalls be raked and dusted with pulverized limestone. These are practices that have been in place within the on -site wastewater industry to help loosen the soil and aid in restoration of soil structure. I am pleased to be of service in this matter and can be contacted at questions concerning information within this report. Thank you, -� a Scott Cole North Carolina Licensed Soil Scientist should you have any rrN I_(_j' 'Ti { { '--� —Bey:____• Proposed Stormwater BMP #3 i a f' SHWT: 9' bgs SHWT Elevation: 184' Ksat 0-36" SL: 8" 1 hour _ - Ksat 36"+ SCL (heavy): Not Measured Proposed Stormwater BMP #4 SHWT: 9' bgs \• «,,.. jr �/` .�' �\::,..� SHWT Elevation: 197' �• �`° �•, Ksat 0-24" SCL: 2.5" 1 hour Ksat 24"-48" SC: .2" / hour Ksat 48"+ Expansive Clay: Not Measured , us r7,� �, `, f, ;{ tiff r ;1 � . � z l � ,_ � 1•.,� `' � i Tz .--� Proposed Stormwater BMP #2 =•-�=F:•Ea SHWT: 10' bgs SHWT Elevation: 189" �\ 1 •��'.► Ksat 0-24" SL: 8" / hour M£.. { Ksat 24"-50" SCL (heavy): 2.5" / hour (� { i:= Ksat 50"+ Expansive Clay: Not Measured k i Proposed Stormwater BMP #1 ' ,.._.,X orri _r SHWT: 11' bgs SHWT Elevation: 205' Ksat 0-18" SL: 8" / hour Ksat 18"-50" SCL (heavy): 2.5" / hour '{ Ksat 50"+ Expansive Clay: Not Measured \ 1 inch = 300 feet