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SU0002741 SSNL
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SU0002741 SSNL
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Entry Properties
Last modified
12/2/2019 8:32:46 AM
Creation date
9/9/2019 10:20:31 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0002741
PE
2633
FACILITY_NAME
SA-98-59
STREET_NUMBER
15908
Direction
S
STREET_NAME
STEINEGUL
STREET_TYPE
RD
City
ESCALON
ENTERED_DATE
11/1/2001 12:00:00 AM
SITE_LOCATION
15908 S STEINEGUL RD
QC Status
Approved
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SJGOV\sballwahn
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\MIGRATIONS\S\STEINEGUL\15908\SA-98-59\SU0002741\NL STDY.PDF
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EHD - Public
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Soil Physical Properties & Suitability Analysis To Receive Agricultural Waste: <br /> Properties currently farmed with this dairy operation: <br /> Properties Owned: <br /> APN# Total Acres Farmed Acres <br /> 229-12-34 78.26 52.3 <br /> 229-12-32 9.79 6 <br /> 229-12-33 9.79 9 <br /> 229-12-18 39.63 38 <br /> 229-12-16 19.97 19 <br /> Properties Rented: <br /> 229-13-03 85 <br /> 229-12-30 21.45 19 <br /> Total farmed acres: 228.3 <br /> Note: The capability of soil to receive agricultural waste is classified in three categories:slight, <br /> moderate and severe. Each labeling the soils' capability limitations to the applications of agricultural <br /> Two soil samples were selected from boring MDS-I for physical properties analysis. The samples were <br /> left in the two by six inch brass or stainless steel sleeves and submitted to Sierra Testing laboratories in EI <br /> Dorado Hills,California. The samples were tested,as received in the sleeves for Flexible-wall <br /> Permeability using ASTM Method#D5084. After completion of the permeability tests,the samples were <br /> removed from the sleeves and subjected to a size analysis using sieves and hydrometer(ASTM Method <br /> #D422). <br /> Findings: <br /> Soil Profile: <br /> Two water supply wells were installed on the Manuel Da Silva property. One of these were installed at <br /> the dairy sand one at the Manuel Da Silva residence. The residence well was completed on October 7, <br /> 1993,to a depth of 245 feet,where as,the dairy well attained a depth of 245 feet on September 1, 1995. <br /> Logs of both of these wells show a lithology dominated by enterlayered sand and clay. The residence well <br /> intersected coarse sand and gravel layers at depths of 80 to 94 and 107 to I I 1 feet below the surface. The <br /> dairy well encountered these coarse-grained units from 75 to 80 feet and 110 to 135 feet. (See appendix <br /> A). <br /> The soil borings carried out in the present study allow a more precise definition of these sediments <br /> down to a depth of 40 feet. In the boring MDS-1, which was drilled adjacent to the present holding pond, <br /> the sediments are dominated by an upper sequence of clayey sands down to a depth of approximately <br /> twenty one feet below surface. Below this level,down to the total hole depth of 41.5 feet,the sediments <br /> consist of silts and clayey silts. A thin layer of clayey sand is present near the bottom of the boring. <br /> The sedimentary sequence on MDS-2 is dominated by sand,with silt and clay layers. The thickest of <br /> these fine-grained sediments is present from approximately 21 to 28 feet below ground surface. A layer of <br /> hardpan is present from one to three feet in depth. <br /> Soil Analytical Results: <br /> Nitrate and TKN <br /> Analytical results of soil samples for TKN from MDS-1 show none detected values for all samples <br /> collected. Damoles analyzed for nitrate show consistent values of about 30 mg/Kg in the upper sandy <br /> sequence down t twenty feet below ground surface. At 25 feet the citrate values increase to maximum of <br /> 43 mg/Kg. However,below this level,nitrate concentrations decrease and the last sample, at 40 feet, <br /> shows none detected levels of nitrate. <br /> These data are interpreted as nitrate levels in the upper sandy sedimentary sequence as a result of <br /> leaching from land application of animal waste or lateral migration from the waste impoundment. The <br /> higher level of nitrate at 25 feet indicates pounding at the top of the clayey silt layer and decrease of <br /> nitrate below that level down to non detect at 40 feet shows that the clayey silt layer is preventing the <br /> downward infiltration of nitrate below that level. <br /> 6 <br />
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