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SU0008978 SSNL
Environmental Health - Public
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SU0008978 SSNL
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Last modified
5/7/2020 11:33:47 AM
Creation date
9/9/2019 9:03:47 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0008978
PE
2631
FACILITY_NAME
PA-1100122
STREET_NUMBER
16261
Direction
E
STREET_NAME
RIVER
STREET_TYPE
RD
City
RIPON
Zip
95366
APN
24519017
ENTERED_DATE
11/21/2011 12:00:00 AM
SITE_LOCATION
16261 E RIVER RD
RECEIVED_DATE
11/21/2011 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\rtan
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FilePath
\MIGRATIONS\R\RIVER\16261\PA-1100122\SU0008978\NL STDY.PDF
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EHD - Public
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LUCCA WINERY <br /> SOIL SUITABILITY & NITRATE LOADING STUDY MAY 2013 <br /> NLS§ 3.3 Table 1 below summarizes the subsurface soil characteristics encountered <br /> from the two sample depths below grade: <br /> Table 1 — Soil Profile Characteristics and Analytical Test Results <br /> Soil Profile Characteristics and Analytical Test Results <br /> Sample Depth Soil Nitrogen Content NO3-N Cation Exchange Capacity, Soil <br /> Below Ground <br /> Surface ft (ppm) CEC (meq/100g) pH Classification' <br /> 3.0 4.0 5.7 5.7 Loamy Sand <br /> 7.0 1.0 5.8 6.6 1 Loamy Sand <br /> Note 1. Soil Classification per the NRCS Map Unit Description of Delhi Loamy Sand <br /> C. Percolation Test Results <br /> SSS§ 6.2. To assess the permeability of the on-site soils, two percolation test borings <br /> were completed in the proposed leachfield location as depicted in the Site Plan found in <br /> Appendix B. The "EHD Official' perc test depth at 36 inches below existing grade gives <br /> a comparatively detailed observation of subsurface permeability from approximately 30 <br /> to 36 inches in depth. The second depth at 84 inches below existing grade provided a <br /> detailed observation of subsurface conditions in regards to the effects of deep <br /> percolation of water and denitrification due to the porous soils. As noted in Table 2 <br /> below, both test borings possess rapid permeability. <br /> SSS§ 6.3. On December 13, 2013, the perc test borings were drilled in the referenced <br /> locations. The sidewalls of the borings were scored with a pry-bar to open potentially <br /> smeared sidewalls. Two inches of fine gravel was placed at the bottom and four-inch <br /> perforated PVC pipe was inserted in the two borings. The test borings were pre- <br /> saturated with 12 inches of water at 0900 hrs, 24 hrs before the start of testing. <br /> SSS§ 6.4, 6.5. On December 14, 2013, percolation testing commenced. No standing <br /> water was observed after the 24-hr soak period in either test boring. Consequently, <br /> EHD Perc Test Procedure #2 was conducted initially in which testing was done over a <br /> four-hour period to induce maximum soil saturation. <br /> When the test was commenced, the percolation rate did not leave standing water at the <br /> 30 minute mark. Upon the initiation of the test, EHD sanitarian Ted Tasiopolous, REHS <br /> reviewed the percolation rate and authorized EHD Perc Test Procedure #3, in which the <br /> test was performed over a one-hour period. The test results indicate a perc rate at 1.9 <br /> minutes per inch (min/in) for the 3 foot depth test boring and 6.7 (min/in) for the 7 foot <br /> depth test boring. The percolation test rate form can be found in Appendix E, A <br /> summary of the perc test results with corresponding application rates in gallons of <br /> effluent accepted per square foot of soil, per day are found in Table 2: <br /> Page 14 <br />
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