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SU0005186_SSNL
EnvironmentalHealth
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99 (STATE ROUTE 99)
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2600 - Land Use Program
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PA-0500401
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SU0005186_SSNL
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Last modified
11/19/2024 1:52:16 PM
Creation date
9/8/2019 12:49:21 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0005186
PE
2611
FACILITY_NAME
PA-0500401
STREET_NUMBER
10748
Direction
N
STREET_NAME
STATE ROUTE 99
City
STOCKTON
APN
08607006 & 07
ENTERED_DATE
7/6/2005 12:00:00 AM
SITE_LOCATION
10748 N HWY 99
RECEIVED_DATE
7/6/2005 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\sballwahn
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FilePath
\MIGRATIONS\N\HWY 99\10748\PA-0500401\SU0005186\NL STDY.PDF
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EHD - Public
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u � <br /> FFand <br /> uents listed above also play a role in the denitrification capacity of the underlying soil, <br /> the results of this Study and previous domestic well water tests conducted by EHD, <br /> e significant. Denitrification capacity is predominately dependant upon: 1.)Abundance <br /> ic carbon substrate, 2.)High soil moisture content leading to an anaerobic environment, <br /> h soil pH (alkaline). The organic matter content of the subsurface soils are of a low <br /> percentage which was to be expected; however, the pH is alkaline for all of the soil samples. <br /> During the drilling procedures of the exploratory borings,very moist-to-wet soil moisture <br /> conditions were observed, thus creating the potential for an anaerobic environment. This high soil <br /> moisture condition can be attributed to the high amount of rainfall during the winter of 2004/2005. <br /> NLS§1.2 In addition to the analytical chemistry completed on the soil samples, Particle Size <br /> Analysis was also done on the exploratory samples as denoted on the Soil Analysis Reports. These <br /> soils have been classified by A&L Laboratory under the United States Department of Agriculture - <br /> Natural Resources Conservation Service(USDA-NRCS) classification(e.g., sandy loam, loam, <br /> etc.). The Unified Soil Classification System(USCS - e.g., lean clay, silty clay CL-ML/CL) has <br /> been used on each of the EHD Percolation Test Rate Field Forms to identify the soil as <br /> encountered in the percolation test borings for each individual Lot. <br /> Nitrogen in septic tank effluent consists of approximately 75%N in the ammonium ion (NH4') <br /> form and 25%N in the organic form. If the ammonium ion is bound and eventually utilized by <br /> microorganisms, nitrification cannot occur. The pH, along with the Cation Exchange Capacity <br /> (CEC),have significant influence on ammonium. The CEC measures the ability of the soil to <br /> theoretically trap, hold and convert ammonium molecules. Soil profiles from both borings have a <br /> medium CEC of approximately 15,which should slightly increase the retention of ammonium <br /> molecules for microbial uptake and suppression of nitrification. <br /> The test results for the important constituents contributing to nitrate formation are tabulated and <br /> summarized in Table 1 below. hl addition,the soil texture descriptions from each sample depth <br /> are also denoted for comparison purposes. SSS§ 5.2, 5.3, 5.4 <br /> TABLE 1 <br /> SELECTED SOIL PROFILE DATA UNDER <br /> FALLOW LAND AREA OF PROPOSED LOT 3 and LOT 10 <br /> 110111111 <br /> Soil Sample Depth Nitrate-Nitrogen Soil Soil Description <br /> and Location Concentration pH/CEC Texture <br /> 5 it 3 ppm 8.6/15.7 57%Sand <br /> Under Proposed Lot 3 22%Silt Sandy Clay Loam <br /> Sample 113;5FT-3 20%Clay <br /> loft 3 ppm 8.5/10.5 37%Sand <br /> Under Proposed Lot 3 34%Silt Clay Loam <br /> Sample m: l OFT3 28%Clay <br /> 15 ft 4 ppm 8.5/14.2 69%Sand <br /> Under Proposed Lot 3 18%Silt Sandv Loam <br /> Sample m:15FT3 12%Clay <br /> Page-3- <br /> Chesney Consulting <br />
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