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SU0002754 SSNL
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SU0002754 SSNL
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Entry Properties
Last modified
5/7/2020 11:29:27 AM
Creation date
9/5/2019 10:57:28 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0002754
PE
2633
FACILITY_NAME
SA-98-72
STREET_NUMBER
10720
Direction
S
STREET_NAME
HARLAN
STREET_TYPE
RD
City
FRENCH CAMP
APN
19327016
ENTERED_DATE
11/1/2001 12:00:00 AM
SITE_LOCATION
10720 S HARLAN RD
QC Status
Approved
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SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\H\HARLAN\10720\SA-98-72\SU0002754\NL STDY.PDF
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EHD - Public
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a <br /> IMPACT MITIGATION <br /> Nitrate-nitrogen impact from a future septic system expansion must be mitigated by the <br /> following design: First,by using two - 1,600 gallon septic tanks in series,there will be a higher <br /> percentage of solid organic material trapped within the tanks. Additionally, a filter should be <br /> installed on the last tank(e.g. Zabel®or OSIC Filters)before the effluent flows (or is pumped) <br /> _ to the leachfield. There is evidence that septic tanks have the capability to denitrify nitrate: As <br /> influent enters the first tank, the wastewater has been aerated from flushing action, and from the <br /> aerator on a faucet, etc. But as the oxygen is consumed by microbiological processes, the tank <br /> becomes anaerobic and the microbes begin to use nitrate as an electron acceptor. When the <br /> effluent reaches the second tank, there is virtually no oxygen within the tank contents, thus <br /> theoretically promoting denitrification `I . <br /> I' ,AC,IA GKtS / 6 - <br /> The leachlines should be placed as hif 01.0 _k n' L line trench, preferably 12 <br /> inches below grade. Filter beds may I C f r,„ However, there must be a <br /> 100% replacement area incorporated i <br /> IV. CONCLUSIONS AND Ith 1v11v1r,1N1.ri i IONS <br /> It is our opinion the subject site is suitable for its intended use with regard to septic effluent <br /> management and that potential environmental impact from future nitrate-nitrogen loading has <br /> been mitigated to an acceptable extent. <br /> The percolation rates obtained indicate a permeable soil. Effluent management is based on the <br /> permeability of the soil eventually reaching an long term application rate (LTAR) of <br /> approximately 0.5 to 1.0 gals/ftl/day due to biomat formation. It is imperative that if a repair <br /> is made or an additional system installed, the underlying hardpan layer must be completely <br /> breached and removed before leachtine emplacement. Sumps should also be used if there <br /> is an increase in the number of people using the system, leading to greater wastewater flows <br /> than those anticipated in this report. <br /> Without sophisticated groundwater monitoring over a long period of time, it is unknown as to the <br /> exact groundwater depth at different times of the year, as well as the groundwater directional <br /> flow. However, sufficient data has been collected and analyzed to determine that the <br /> groundwater table is currently an acceptable distance below grade for there to be adequate <br /> biological treatment, according to published scientific literature. Groundwater analyses of the <br /> on-site domestic well indicates a medium nitrate impact to the underlying drinking water <br /> aquifers. <br /> Mounding effects under the leachfields should be of no concern since the saturated zone is at a <br /> sufficient depth. <br /> 6 <br /> Vaffey Ag Rgsearch <br />
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