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SU0000021 SSNL
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MS-01-14
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SU0000021 SSNL
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Entry Properties
Last modified
5/7/2020 11:27:33 AM
Creation date
9/6/2019 10:13:55 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0000021
PE
2622
FACILITY_NAME
MS-01-14
STREET_NUMBER
15444
Direction
S
STREET_NAME
MITCHELL
STREET_TYPE
RD
ENTERED_DATE
8/8/2001 12:00:00 AM
SITE_LOCATION
15444 S MITCHELL RD
RECEIVED_DATE
4/13/2001 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\M\MITCHELL\15444\MS-01-14\SU0000021\NL STDY.PDF
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EHD - Public
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v <br /> 2.7 in/yr 32 MR NIL CL--0.251+ (t I in/yr x 0.1 mg/L) ,. <br /> Nr = (2.7 in/yr+ 11 in/yr) <br /> Nr = 5 ppm as NO3-N <br /> E. COMPARISON BETWEEN AGRONOMIC INPUT IF PROPERTY.REMAINED IN <br /> AGRICULTURAL PRODUCTION VERSUS PROPOSED DEVELOPMENT OF THE PROJECT. <br /> As referenced above, the two proposed Parcels are currently planted in six-year-old almond trees. <br /> Consequently, comparison shall be made between nitrate impact from the fertilization of 4.5 <br /> acres of almond trees vs. nitrate impact from the proposed development of two SFRs on this <br /> same 4.5 acres. Calculated nitrate impact from the two SFRs was estimated to be 5 ppm NO3-N. <br /> Therefore, the question is: What concentration of nitrate from fertilizer and organic matter is not <br /> taken up by the almond tree root system and leaches past the root zone? There are a number of <br /> computer programs available to analyze this question, most notably NLEAP -Nitrate Leaching <br /> and Economic Analysis Package. However, nitrate-nitrogen'loading originating from the <br /> existing almond orchard will be based upon analytical test results and calculatedprojections 4 <br /> during the growing season. It is important to note that these test results were of course, obtained <br /> at the end of the growing season. The majority of nitrate-nitrogen leaching occurs during the <br /> growing season, especially in sandier soils. Although there will be some hindrance of the <br /> downward migration of nitrate from the hardpan stratum, this strata is intermittent according to <br /> Mr. Sephos who has farmed this area for several years. As noted, the soil structure becomes <br /> increasiay sandier with depth, thus acceleratin the downward movement of nitrate, <br /> particularly with flood irriatron. <br /> Nitrogen loading analysis starts at the beginning of the growing season in the springtime. Mr. <br /> Sephos applies a total of 200 units (200 lbs/ac) of ammonium nitrate over the course of the <br /> growing season, in four equally-timed applications of 50 units each(assume ammonium is taken <br /> up by the trees or converted to nitrate for uptake or leaching). According to the Western <br /> Fertilizer Handbook(Table 4-1), almond trees require 200 lbs of nitrogen per acre yieelld of <br /> 3000w.lbsI,so the„,xutroge aplzcations maw besomevvhat high forsiyea old trees. <br /> Nitrogen applications are water-run by flood irrigation. Unlike drip or micro-sprinkler irrigation <br /> where the irrigation water and nutrients are applied directly to the spatial orientation of the tree <br /> roots, flooirrigation allows a grcentnge of water and nutrients to by-passaree roots that do not <br /> extend out into the middle rows (rows between trees rows). This leaching percentage can be <br /> anywhere from 15%to 30%. Consequently, a higher concentration of nitrogen must be applied <br /> to counteract this leaching loss. <br /> As referenced in Section II B-1, chemical analysis was done to quantify NO3-N (and other <br /> constituent) concentrations at three soil horizon depths: 40 inch, 6 ft and 12 ft. As noted on the <br /> SOIL ANALYSIS REPORT, the concentrations of NO3-N are 4 ppm, 3 ppm and 3 ppm for <br /> each respective depth. Focus is placed on the NO3-N concentration of 3 ppm from 6 ft to 12 ft, <br /> since this is theoretically below the root zone. <br /> 9 <br /> VaderJ. Ag research <br />
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