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SR0078011 SSNL
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SR0078011 SSNL
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Entry Properties
Last modified
1/8/2020 9:53:24 AM
Creation date
9/4/2019 10:25:23 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0078011
PE
2601
STREET_NUMBER
25526
Direction
S
STREET_NAME
BIRD
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
23919027
ENTERED_DATE
8/4/2017 12:00:00 AM
SITE_LOCATION
25526 S BIRD RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\sballwahn
Supplemental fields
FilePath
\MIGRATIONS\B\BIRD\25526\NL STUDY.PDF
Tags
EHD - Public
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NLS§ 1.2. Noted on the attached Soil Analysis Report,the chemical analyses conducted quantifies <br /> several constituents that influence nitrate loading for this project. The important parameters for <br /> nitrate loading assessment are the organic matter and estimated nitrogen release (ENR), clay <br /> content,pH, cation exchange capacity(CEC),and the nitrate-nitrogen content of the soil. The <br /> organic matter is medium at 2.8%. The ENR is 85 lbs/ac. This OM and ENR concentrations <br /> suggest there is aaj1pR2Lmediuni potential for future nitrate forming from organic matter., As <br /> nitrate molecules that may form from the septic effluent percolate downward, these molecules <br /> travel into and through the clay soil. This soil type is generally anaerobic because of the soil <br /> micropores, thus promoting denitrification and inhibiting nitrification. Since septic effluent is <br /> composed predominately of ammonium (NH4),the pH, along with the CEC, have significant <br /> influence on ammonium molecules. <br /> The pH of the soil is very slightly alkaline at 7.1 which won't have much of an effect in promoting <br /> ammonia formation or ammonium formation. Since ammonium is the precursor to nitrate, <br /> ammonia(NH,)may be slightly promoted, which may retard ammonium (NH4) formation. The <br /> CEC measures the ability of the soil to theoretically trap and hold ammonium molecules and was <br /> measured at 23.9 meq/100 g,which is a high value. This suggests a high potential for the retention <br /> of ammonium molecules for microbial assimilation within the soil. The nitrate-nitrogen is a <br /> medium concentration at 22 ppm, indicating a medium potential for nitrate leaching,but <br /> simultaneously a high potential for denitrification within the high clay content soil. <br /> NLS§ 3.3. Table 1 below summarizes the analyzed soil physical and chemical characteristics <br /> from the retrieved soil sample: <br /> TABLE 1 <br /> SOIL PROFILE CHARACTERISTICS AND <br /> ANALYTICAL TEST RESULTS <br /> SANIPLE DEPIII SOIL TEXTURE. SOIL NITRATE- pH AND <br /> CLASSIFICATION NITROGEN CONTENT CATION EXCHANGE CAPACITY <br /> In meq/100g <br /> 361N.DEPTH <br /> Clay 22 ppm NO -N 7.1 21.2 me /100 <br /> GROUNDWATER INFORMATION <br /> NLS§ 2.1. Groundwater depths and elevations throughout San Joaquin County are illustrated on <br /> maps published by the County Flood Control and Water Conservation District. The Fall 2016 <br /> Lines of Equal Depth Map and the Lines of Equal Elevation Map indicate groundwater depth and <br /> directional flow. Depth to groundwater is approximately 60 ft below grade and the groundwater <br /> directional flow appears to be in a north-northeasterly direction. <br /> NLS§2.2,3.1. Surrounding agricultural properties are currently farmed and have been for <br /> decades, and surrounding residential properties are on septic systems so the potential for nitrate <br /> contamination of the underlying groundwater can be considered significant. <br /> Page 2 of 13 <br />
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