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SU0000638 SSNL
Environmental Health - Public
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SU0000638 SSNL
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Entry Properties
Last modified
5/7/2020 11:27:51 AM
Creation date
9/4/2019 6:39:40 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0000638
PE
2622
FACILITY_NAME
MS-96-15
STREET_NUMBER
23400
Direction
S
STREET_NAME
FREDERICK
STREET_TYPE
AVE
City
RIPON
ENTERED_DATE
9/24/2001 12:00:00 AM
SITE_LOCATION
23400 S FREDERICK AVE
QC Status
Approved
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SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\F\FREDERICK\23400\MS-96-15\SU0000638\SS STDY.PDF
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EHD - Public
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161 CONCLUSIONS <br /> �- The percolation rates for the subject property illustrate that a septic system with a 6,000 to 8,000 <br /> square foot leachfield may be utilized for a mobile home or new residential structure to be built on <br /> Parcel 2. An 8,000 square foot leaching area is recommended if there is potential influence from a <br /> hardpan layer. This will be detected during the installation of the septic system. The number of <br /> Permit Applications for additional leachline would indicate a larger leachfield should be installed. <br /> Although we do not have knowledge at this point in time as to the size or number of bedrooms <br /> the new structure will have, this will also have to be taken into consideration for the final design <br /> of the leachfield. For example, a four bedroom house should have between 8,000 and 10,000 <br /> i' square feet of leachfield area. A 50% standby replacement area must also be incorporated into <br /> a the design. The referenced leachfield areas will help ensure stability and guard against leachfield <br /> failure. A failure would primarily result from the formation of a "biomat" or "clogging mat" on <br /> the wetted soil where the effluent enters the soil. This mat is composed mostly of aerobic and <br /> 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. This type of biological activity <br /> will probably prevail due to the sandy nature of the leachfield area soil. <br /> ' With respect to the protection of the underlying groundwater from pathogens and nitrates (NO3), <br /> ' the shallow depth to groundwater (-18 ft) and the sandy soil structure can be considered a <br /> favorable environment for nitrate and DBCP continued contamination. The attached well logs <br /> indicate there is a clay layer between grade and the depth to groundwater and this may have some <br /> &W attenuation effect on the downward migration of nitrate molecules. However, the high amount of <br /> agricultural activity and consequently nitrogen fertilization in the area will certainly contribute <br /> L. nitrates to the underlying groundwater to a much greater extent than will the low density housing <br /> in the area. <br /> W <br /> All related septic system structures and the domestic well will have to comply with the published <br /> "distance" requirements from property borders, roads, irrigation fields, etc. <br /> � X1°0 $ ��uulity `Joniro� �xspection <br />
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