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SR0082378_SSNL
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SR0082378_SSNL
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Last modified
9/1/2020 4:25:35 PM
Creation date
9/1/2020 4:10:49 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0082378
PE
2602
STREET_NUMBER
18700
Direction
E
STREET_NAME
RIVER
STREET_TYPE
RD
City
RIPON
Zip
95366
APN
24522028
ENTERED_DATE
7/27/2020 12:00:00 AM
SITE_LOCATION
18700 E RIVER RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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TSok
Tags
EHD - Public
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TABLE 3 <br /> WINERY DOMESTIC WELL: <br /> ANALYTICAL RESULTS OF TESTED CONSTITUENTS <br /> SAMPLE ID NITRITE AS NITROGEN TKN/NH., TOTAL ALKALINITY pH/Ec <br /> t <br /> Well 24.7 mg/L ND 190 mg/L 7.59/682 umhos/cm <br /> MCL= 10 mg/L Non-Detect <br /> Calculation on the Alkalinity Requirement for Nitrification <br /> The nitrate-nitrogen loading calculations are contingent upon the environmental factors required <br /> for nitrification to occur. These conditions include soil pore-space oxygen content, soil <br /> temperature, pH, electrical conductivity, organic matter, cation exchange capacity, and alkalinity. <br /> Alkalinity in wastewater effluent is derived from the water source, in addition to the introduction <br /> of wastes. Nitrification consumes approximately 7.1 mg of alkalinity for every mg of ammonia- <br /> nitrogen (NH4-N) oxidized. Nitrification of the Total Kjeldahl Nitrogen (TKN) concentration of <br /> 223 mg/L, as determined below, would require: 223 mg/L NH4-N x 7.1 mg CaCO3 = 1,583 mg/L <br /> alkalinity. The alkalinity in the well water was determined to be 190 mg/L. The alkalinity <br /> determined from the septic tank effluent sample (A&L Laboratories) was 983 mg/L. 190 + 983 = <br /> 1,173 mg/L alkalinity. Therefore, an approximate deficient value of 1,583 mg/L - 1,173 mg/L = <br /> 410 mg/L of additional alkalinity must come from soil alkalinity, or another source to provide a <br /> sufficient concentration for complete nitrification of the effluent to occur. <br /> E. SURFACE WATER INFORMATION AND CALCULATIONS <br /> NLS§3.2. As referenced, the subject facility occupies two full APN Parcels and a partial third <br /> APN Parcel. For the Nitrate Loading Study, this acreage does not include surrounding vineyards <br /> and orchards that are part of the winery property,which totals 89.18 acres. The acreage of the <br /> winery facility exclusively is 48.4 acres. The actual winery facility(buildings, tank farms, concrete <br /> paved areas, etc.) and the lined wastewater treatment/stormwater ponds total 12.6 acres. This 12.6 <br /> acre area is considered impervious. The remaining area is specified as gravel and undeveloped <br /> areas, which can be considered pervious, and totals 35.8 acres. The existing leachfield area is 0.97 <br /> acres of this 35.8 pervious acres. These land use designated areas are delineated in the Site Plans <br /> produced by Advanced Design Group. <br /> The following Mass Balance Approach utilizes these referenced area delineations correlated with <br /> Available Rainfall and Net Rainfall Recharge: <br /> Available Rainfall= 13.5" (1.13 ft) <br /> Net Rainfall Recharge= 10.0" (0.833 ft)26%reduction based on the gross area correlated with the <br /> reduction in area of the pervious area. <br /> Pervious area: Undeveloped, open areas=35.8 ac: <br /> 35.8 ac x 325,851 gals/ac-ft x 0.833 ft=9,717,333 gals (R1) <br /> Page -5- <br /> Chesney Consulting <br />
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