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SR0082378_SSNL
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SR0082378_SSNL
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Entry Properties
Last modified
9/1/2020 4:25:35 PM
Creation date
9/1/2020 4:10:49 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0082378
PE
2602
STREET_NUMBER
18700
Direction
E
STREET_NAME
RIVER
STREET_TYPE
RD
City
RIPON
Zip
95366
APN
24522028
ENTERED_DATE
7/27/2020 12:00:00 AM
SITE_LOCATION
18700 E RIVER RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
TSok
Tags
EHD - Public
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r�2The organic matter in the perc test borings are low and very low, with the east end of the leachfield <br /> possessing twice the O. M. content than the west end. The nitrate-nitrogen concentrations reveal <br /> interesting results with the west end of the leachfield with twice the concentration of nitrate-nitrogen <br /> as the east end. It can be theorized that due to the increase in O.M. percentage at the east end,this <br /> has promoted denitrification and lowered the nitrate-nitrogen concentration at the east end by 50%. <br /> The pH of the soils is slightly acidic at 6.8/6.7 which will promote ammonium formation. However, <br /> ammonium molecular retention within clay micro-sites will be limited due to the relatively low clay <br /> content. The CEC is 5.1/5.7 which would be expected given the soil texture analysis of a sandy <br /> loam. A low CEC theoretically has a lower potential for adsorbing ammonium molecules. The clay <br /> content of the soil at 11% indicates a sufficient percentage of clay to maintain biochemical processes <br /> and mitigate a rapid perc rate. <br /> The backhoe test pit soil samples alsd reveal low O.M. percentages, as well as a slightly alkaline soil. <br /> The CEC is what is to be expected,with a very low concentration due to the sand soil at 12 ft. of <br /> interest, is the dramatic decrease in nitrate-nitrogen concentration of 23 ppm down to 3 ppm from 8 <br /> ft to 12 ft depth; an 87%decrease. This may be due to anaerobic conditions due to saturation where <br /> the loamy sand transitions to sand,thus promoting denitrification; or the nitrate-nitrogen molecules <br /> have quickly traveled through the sand. This is unlikely however, given the nitrate concentration <br /> directly above this sand stratum that would continually supply nitrate. <br /> NLS§3.3, SSS§5.3, 5.4. Table 1 below summarizes the analyzed soil physical and chemical <br /> characteristics from the retrieved soil samples: <br /> TABLE 1 <br /> SOIL PROFILE CHARACTERISTICS AND <br /> ANALYTICAL TEST RESULTS <br /> SAMPLE I.D.DEPTH SOIL TEXTURE SOIL NITRATE- pH AND <br /> CLASSIFICATION NITROGEN CATION EXCHANGE CAPACITY <br /> CONTENT In meq/100g <br /> LFW40 Sandy Loam 6 ppm NO;-N 6.8 5.1 meq/1008 <br /> (Leachfield West 40"Depth) (SM,ML) <br /> LFE40 Sandy Loam 3 ppm NO;-N 6.7 5.7 meq/100(, <br /> (L eachfield East 40"Depth) (SM,ML) <br /> BTP8 Loamy Sand 23 ppm NO;-N 7.1 6.5 meq/100(, <br /> (Backhoe Test Pit 8 ft Depth) (ML,SM) <br /> BTP12 Sand 3 ppm NO;-N 7.5 2.4 meq/IOOg <br /> (Backhoe Test Pit 8 ft Depth) (SW) <br /> C. PERCOLATION TEST RESULTS <br /> SSS§6.2. As referenced,to assess the permeability of the existing shallow leachline soils, <br /> percolation test borings were completed at the east and west ends of the leachfield. Test locations <br /> are depicted on the project Site Plan produced by Advanced Design, Inc. <br /> Page -3- <br /> Chesney Consultimo <br />
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