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SU0003053 SSNL
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SU0003053 SSNL
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Last modified
5/7/2020 11:29:38 AM
Creation date
9/6/2019 10:34:44 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0003053
PE
2633
FACILITY_NAME
SA-94-28
STREET_NUMBER
28864
Direction
S
STREET_NAME
KASSON
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
24138002
ENTERED_DATE
11/6/2001 12:00:00 AM
SITE_LOCATION
28864 S KASSON RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\K\KASSON\28864\SA-94-28\SU0003053\NL STDY.PDF
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EHD - Public
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Manure Application <br /> INTRODUCTION thought to be caused by germination moval per unit of yield for many <br /> damage and growth reductions due crops. Actual removal will be site <br /> Manure is a co-product of animal to high concentrations of ammonium specific and may be determined by <br /> agriculture. Depending on the point and soluble salts including sodium, a laboratory analysis of a represen- <br /> of view, it is either a resource for potassium, magnesium, calcium, tative sample of the plant material <br /> crop production or it is a waste prod- and chloride, which can limit water removed from the field. <br /> uct of the livestock enterprise. No uptake by the plants. <br /> matter what the point of view, it must NUTRIENT AVAILABILITY <br /> be removed to continue the livestock High salt level can also cause <br /> operation. Soils normally benefit injury to plant root hairs which will The nutrients contained in ani- <br /> from the application of organic ma- result in reduced nutrient and water mal manures, composts, or other or- <br /> terial and animal manure is an ex- uptake. Also, improper balance be- ganic materials are less readily avail- <br /> cellent source. This organic mate- tween sodium in relation to calcium able to plants than the nutrients of <br /> rial acts as a source of nutrients and and magnesium will cause soil ag- most inorganic fertilizers. The nutri- <br /> as a soil conditioner. Therefore, it gregates to break down or disperse. ent content of these materials is <br /> makes sense to use manure to re- The dispersed clay particles will highly variable (Table 2) and a labo- <br /> cycle nutrients and improve the soil. move down into the soil profile, ratory analysis should be used to de- <br /> blocking soil pores, reducing the rate termine the actual nutrient content <br /> It is difficult to place a dollar value of water infiltration. of manure materials. <br /> on the improvements in physical <br /> properties of the soil from the addi- NUTRIENT REQUIREMENTS NITROGEN: Manure would be clas- <br /> tion of manure, but the value can be sified as a slow release nitrogen fer- <br /> considerable when evaluated on a Before manure is applied,the nu- tilizer. Approximate manure nitrogen <br /> long term basis. trient requirement of the crop should availability percentages are listed in <br /> be determined. Soil testing is a reli- Table 3. They vary according to the <br /> The main value of manure is its able method to determine nutrient type of material, storage, and appli- <br /> supply of nitrogen, phosphorus, and levels in the soil. With this informa- cation method. When incorporated, <br /> potassium. Micronutrients will also tion, and knowledge of the nutrient most of the ammonium nitrogen is i <br /> be available, but the amounts will levels of the manure, economically available during the first year. Nitro- <br /> G <br /> vary greatly depending on type of and environmentally sound applica- gen availability percentages listed in <br /> livestock and their diet. tion rates for both manure and fertil- Table 3 are total N and account for <br /> izer can be determined. ammonium nitrogen content. The <br /> About half of the nitrogen is in figures in Table 3 are based on avail- <br /> the inorganic or ammonium form,the Manure application rates are ability of total N during the first year <br /> form that is immediately available for usually based on crop nitrogen re- following a spring application. <br /> plant intake. The inorganic forms of quirements. Manure application <br /> nitrogen are subject to being lost rates should never exceed the crop ORGANIC N (Total N minus ammo- <br /> through leaching out of the root zone nitrogen requirement. However, af- nium N, or assume 60 to 75 percent <br /> or volatilization into the atmosphere. ter long term application, the phos- of the Total N as organic) will supply <br /> Volatilization is minimized by injec- phorus level in the soil will probably nitrogen to the cropping system for <br /> tion or tillage into the soil. build up to a level that will prohibit several years. To estimate residual:} <br /> continued manure applications. All N use the availability factors listed , r <br /> Proper application rates and manure application sites should be in Table 4. <br /> methods must be utilized to ensure monitored with a soil testing pro- <br /> environmentally sound results and gram. To prevent the build up of soil PHOSPHORUS AND POTASSIUM <br /> cost effective application. Excessive phosphorus and potassium levels to About 70 percent of the total P ap- <br /> manure application rates or improper a very high range, it would be best plied in manure will become avail- <br /> application methods can result in to calculate a manure application able in the year of application. Of; r <br /> surface or ground water contamina- rate on basis of crop phosphorus or the total potassium, 100 percent will <br /> tion and reduced crop yields. potassium removal (do not exceed be available the year of application. <br /> crop N requirements). Table 1 pro- <br /> Much of the yield reduction is vides a list of estimated nutrient re- <br />
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