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SU0000578 SSNL
Environmental Health - Public
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MS-97-18
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SU0000578 SSNL
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Last modified
5/7/2020 11:27:49 AM
Creation date
9/9/2019 10:55:27 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0000578
PE
2622
FACILITY_NAME
MS-97-18
STREET_NUMBER
12352
Direction
S
STREET_NAME
VAN ALLEN
STREET_TYPE
RD
City
ESCALON
ENTERED_DATE
9/24/2001 12:00:00 AM
SITE_LOCATION
12352 S VAN ALLEN RD
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\V\VAN ALLEN\12352\MS-97-18\SU0000578\SS STDY.PDF
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EHD - Public
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161 CONCLUSIONS <br /> The percolation rates and the depths at which they were performed illustrate that seepage pits or <br /> possibly sumps will have to be used for any future septic systems on the subject parcels. The <br /> information obtained from the Environmental Health Department concerning the number of <br /> Application permits for seepage pits also indicates a need for this type of septic system. It will be the <br /> determination of the Environmental Health department which type of system may be used. However, <br /> if sumps are installed, we recommend using an "extend-a-hoe" to excavate down to 20+ feet. <br /> Seepage pits may be more cost effective. <br /> The number of seepage pits or sumps for the proposed residence will be dependent upon the number- <br /> _ of bedrooms the structure will have, or the number of occupants, particularly children. The pits <br /> should be at least 33 inches in diameter and installed to a maximum depth of 25 feet. <br /> All related development structures such as wells, leachfields, etc. will have to comply with the <br /> published "distance" requirements from applicable objects such as property borders, crops or ponds. <br /> Each proposed septic system should have a 12,000 square foot leachfield area due to the virtually <br /> non-existent percolation that would occur at the 42 inch depth. A 50% standby replacement area <br /> must also be incorporated into any design. This proposed leachfield area will help ensure stability and <br /> guard against leachfield failure. A failure would primarily result from the formation of a "biomat" or <br /> "clogging mat" on the wetted soil where the effluent enters. This mat is composed mostly of aerobic <br /> and anaerobic bacteria and bacterial products consisting of a slime of polyuronides and <br /> polysaccharides. If the soil/effluent interface is well aerated, a variety of soil microfauna such as <br /> nematodes and protozoa may digest the clogging mat bacteria. However, due to the high clay <br /> content of the shallow soil horizons, anaerobic conditions will most likely prevail. <br /> With respect to the protection of the underlying groundwater from pathogens and nitrates (NO;), the <br /> soil structure of the subject parcels, along with the depth to groundwater, can be considered favorable <br /> for prevention from contamination. The referenced well with high nitrates may be a shallow well with <br /> a poor or non-existent grout seal. It is our opinion that the existing septic systems and any future <br /> residential septic system will have an inconsequential impact on the groundwater due to the following: <br /> The nitrogen cycle and the eventual formation of nitrates are highly complex within the soil <br /> environment. The subject parcel soils are conducive for two beneficial nitrogen cycle processes, <br /> namely fixation of ammonium and denitrification. Fixation of ammonium (NH4) can occur with the <br /> adsorption of ammonium molecules onto expanding clay particles, which is the predominate shallow <br /> Mality &.w Inspection <br />
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