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SU0002671 SSNL
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SU0002671 SSNL
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Entry Properties
Last modified
11/27/2019 11:05:39 AM
Creation date
9/4/2019 6:07:40 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0002671
PE
2633
FACILITY_NAME
SA-99-42
STREET_NUMBER
11655
Direction
S
STREET_NAME
ESCALON BELLOTA
STREET_TYPE
RD
City
ESCALON
ENTERED_DATE
10/31/2001 12:00:00 AM
SITE_LOCATION
11655 S ESCALON BELLOTA RD
QC Status
Approved
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SJGOV\sballwahn
Supplemental fields
FilePath
\MIGRATIONS\E\ESCALON BELLOTA\11655\SA-99-42\SU0002671\NL STDY.PDF
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EHD - Public
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v. r� <br /> 3.) Septic System Contribution: Data from various sources such as independent investigators, <br /> the U.S. EPA, and the Regional Water Quality Control Board estimate nitrogen loadings from <br /> domestic sewage to be 12 grams N per person per day (g Nlcapitalday) to a high of 90 g <br /> N/capitalday. Hantzche and Finnemore (1992) correlated septic tank effluent concentrations <br /> multiplied by water discharge to the septic tank. They formulated a water discharge of 100 <br /> gal/capita/day with an effluent concentration of 30-60 mg NIL. It is our opinion that 60 mg NIL <br /> is most accurate. The following calculations determine nitrate-nitrogen loading from septic <br /> system contributions: <br /> 12 people max. on-site x 100 gals/day = 1200 gals x 3.79 L/gal=4545 L/d x 60 mg NIL = <br /> 273 grins N/day x 365 days/yr= 100 kg Nlyr x 2.2 lb/kg= 220 lbs Nlyr. <br /> 4.) DAIRY NITROGEN PRODUCTION CALCULATIONS <br /> It is important to note that the Borba's plan to sell most of the manure solids produced by the <br /> dairy for off-site use. However,the following calculations demonstrate the facility is completely <br /> self-supporting and may apply both liquid and solid manure forms on all cropland acreage <br /> controlled by the Borba's without overload. The total nitrogen excreted from dairy animals is <br /> difficult to quantify since the rates of several important nitrogen transformation processes can <br /> only be predicted. Secondly, the fact that the animals will be confined under two different <br /> housing structures (loafing vs. freestall) during different times of the year creates differences in <br /> nitrogen loading. The following calculations incorporate the use of animal units (AU) for the <br /> Holstein dairy cow to formulate nitrogen loading. The nitrogen loading calculations for the milk <br /> cows is based on exclusive use of freestalls. The nitrogen loading calculations for the dry stock <br /> is based on exclusive use of the loafing barns with flushed alleys. This provides a more <br /> conservative approach for total nitrogen loading. The animal numbers are the maximum number <br /> the facility can support: <br /> TOTAL ANIMALS ANIMAL UNIT TOTAL ANIMAL UNITS <br /> 1000 Milk Cows x 1.4 = 1400 <br /> 250 Dry Cows x 1.2 = 300 <br /> 500 Bred Heifers x 1.1 = 550 <br /> 270 Heifers 1-2 yr x 1.1 – 297 <br /> 95 Calves x 0.5 = 48 <br /> 40 Baby x 0.25 = 10 <br /> SUBTOTAL MILK COWS AUs ........................................ 1400 <br /> SUBTOTAL DRY STOCK AUs ........................................ 1205 <br /> TOTAL ANIMAL UNITS .................................................. 2605 <br /> 7 —ij <br /> Vaffey Ag*.search <br />
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