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SU0003611 SSNL
Environmental Health - Public
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SU0003611 SSNL
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Last modified
5/7/2020 11:30:05 AM
Creation date
9/8/2019 1:04:07 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0003611
PE
2690
FACILITY_NAME
LA-01-102
STREET_NUMBER
16910
Direction
S
STREET_NAME
NORTH RIPON
STREET_TYPE
RD
City
RIPON
APN
20308022
ENTERED_DATE
5/7/2004 12:00:00 AM
SITE_LOCATION
16910 S NORTH RIPON RD
RECEIVED_DATE
2/19/2002 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\N\NORTH RIPON\16910\LA-01-102\SU0003611\NL_SS STDY.PDF
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EHD - Public
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July 21,2003 <br /> Job Number:LG03-120 <br /> Page 8 <br /> They believe that their method is a good planning tool and provides useful information to <br /> _ planners and local officials but with some real limitations. In their article published in Ground <br /> Water, Hantzsche and Finnemore mention that"...the equation ignores dispersion, lateral flow, <br /> and mixing with ground water flow from up-gradient areas. These processes would generally <br /> contribute to additional reduction of nitrate-nitrogen concentrations in ground water to the extent <br /> that the nitrate-nitrogen concentration of ground-water flow from up-gradient areas is lower."' <br /> The Hantzsche and Fennemore approach"...a conservative (worst case) first approximation of <br /> ground-water nitrate-nitrogen concentration resulting from the combined effect of on-site sewage <br /> disposal systems and precipitation. This (the equation and approach) is for estimation of long- <br /> term effect (i.e., over years) on ground-water quality, and is not intended for prediction of <br /> seasonal changes." <br /> The method takes into account development area, soil denitrification factor, rainfall volume, <br /> rainfall nitrate concentration, the waste effluent quantity, and waste effluent nitrate concentration. <br /> The formula, assumptions and calculations used for the analysis are shown on Plates 8 through <br /> 10. The units of nitrate used in the mass balance equation are nitrate-N whose maximum drinking <br /> water contaminate level is 10 mg/L. <br /> 7.1 Agricultural Fertilizer and Irrigation <br /> Leaching losses of nitrate fertilizer occur when soils have more incoming water(rain or <br /> irrigation)than the soil can hold. As water moves through the soil, the nitrate(NOO that is in <br /> soil solution moves along with the water. Ammonium (NH4') forms of N have a positive charge <br /> and are held by the negative sites on the clay in the soil; therefore,NH,' forms of N leach very <br /> little. In sands where there is very little clay, ammonium forms of N can leach. Coarse-textured <br /> sands and some muck soils are the only soils where ammonium leaching may be significant. One <br /> way to minimize N leaching and denitrification is to minimize the time the N is in the soil before <br /> plant uptake. This cuts down on the time when conditions are favorable for losses.' <br /> According to Angelo Stagnaro, approximately 20 units per acre of N are broadcast on the cherry <br /> orchard and 60 units per acre are applied to the vineyard. The vineyard is on a drip irrigation <br /> system. Walnuts take 60 units or more units Toacre. Irrigation is applied once per week during <br /> the summer for the orchard and none is appy d in the winter. <br /> With the development of residential home, ites,the size of vineyards, cherries, and walnuts may <br /> i <br /> r <br /> -5-ee <br /> 6 <br /> ' Vitosh,M.L.,J. W.Johnson and D.B.Mengel,July 1995.Tri-state Fertilizer Recommendations for <br /> Corn, Soybeans,Wheat and Alfalfa,Extension Bulletin E-2567. <br /> OE RSO <br /> f W <br /> i Iy.SOL♦ <br /> r <br />
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