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SU0000021 SSNL
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MS-01-14
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SU0000021 SSNL
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Entry Properties
Last modified
5/7/2020 11:27:33 AM
Creation date
9/6/2019 10:13:55 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0000021
PE
2622
FACILITY_NAME
MS-01-14
STREET_NUMBER
15444
Direction
S
STREET_NAME
MITCHELL
STREET_TYPE
RD
ENTERED_DATE
8/8/2001 12:00:00 AM
SITE_LOCATION
15444 S MITCHELL RD
RECEIVED_DATE
4/13/2001 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\M\MITCHELL\15444\MS-01-14\SU0000021\NL STDY.PDF
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EHD - Public
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FrTheantzsche/Finnemore Formula predicts a yearly average nitrate-nitrogen concentration in <br /> harge septic effluent from the two proposed SFRs to be 5 ppm NO3-N. The yearly amount <br /> ontrate-nitrogen leaching into the groundwater,from the two SFRs may be as high as 88 lbs <br /> NO3-N. <br /> Fertilizer and organic matter nitrate-nitrogen concentration calculated from the observed <br /> chemical analyses of the soils under the existing almond orchard is 8 ppm NO3-N. The total <br /> yearly amount of nitrate-nitrogen leaching from nitrogen fertilizer applications over the growing <br /> season may be as high as 180 lbs NO3-N. <br /> Therefore, nitrate impact from the proposed development will be theoretically lower than nitrate <br /> impact from the almond tress, both in terms of concentration (5 ppm NO3-N vs. 8 ppm NO3-N) <br /> and amount(88 lbs NO3-N vs. 180 lbs NO3-N). <br /> It is recommended the two wells that will serve the new SFRs be drilled and perforated in deeper <br /> auarant that qst future nitrate ft h m ract willout <br /> shouI extend o at"Ieas 1 rl ft T o.... r;there is no <br /> �.�_ <br /> gp 1 not affect these deeper aquifers. Considering the age of k <br /> the high density housing on Cottage Avenue and the intensity of farming in this area, higher <br /> nitrate levels would have been predicted in these deeper aquifers. <br /> The percolation test results indicate the leachline soils of approximately 40 inches below grade <br /> have a porosity that allows rapid percolation. However, as the soil becomes saturated, the perc <br /> rates noticeably decrease. This rate decrease can be primarily attributed to the underlying <br /> hardpan layer. Therefore, it is recommended that during leachline emplacement, the hardpan <br /> layer should be broken up with a backhoe and backfilled into the leachline trench. This will <br /> allow percolation into the hardpan strata and promote soil saturation. Soil saturation will in-turn <br /> create anaerobic conditions which will stimulate the denitrification process. <br /> Seepage pits are not warranted or allowed in this area. However, sumps or preferably filter beds <br /> can be installed if there are area constraints. As noted on the attached septic system permits, <br /> sumps were installed at the Sephos residence. <br /> It is important to note that all septic systems have a lifespan. This lifespan is dependant on <br /> several factors and is therefore, difficult to determine. If there was septic system failure, it would <br /> probably result from the advanced formation of the biomat on the wetted soil/effluent interface. <br /> This mat is composed mostly of aerobic and anaerobic bacteria and bacterial products consisting <br /> of a slime of polyuronides and polysaccharides. If the soil/effluent interface is well aerated, a <br /> variety of soil microfauna such as nematodes and protozoa may digest the clogging mat bacteria. <br /> Since the shallow subsurface soils consist mostly of a sandier soil material, aerobic conditions <br /> may prevail over time which may inhibit leachline failure. The total length of leachline will be <br /> dependant upon the number of bedrooms each new home will have. Additionally, the system <br /> should be oversized if a number of people, especially children, will inhabit the residences. A <br /> 50%replacement area must be incorporated into the design. <br /> 12 <br /> Naffey Ag Research <br />
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