Table of Contents
Nutrient Content of Dairy Manures
Land
Application
Nutrient
Availability
Application Rate
Timing and Uniformity
of Manure Applications
Calibrating Manure Application
Equipment
Acreage Requirements
for New or Expanding Facilities
Value of Manure
Land Application Worksheet
Prepared
by
J. P. Zublena, Extension Soil Science Specialist;
J. C. Barker, Extension Agricultural Engineering Specialist;
D. P. Wessen, Extension Dairy Science Specialist
Published by
North Carolina Cooperative Extension Service
Publication AG-439-28
Revised
March 1996 (JWM)
Last Web Update:
December 1997 (DBL)
|
Dairy manure and wastewater
are excellent sources of nutrients for most agronomic, horticultural,
and silvicultural crops. Proper management of these manures as nutrient
sources is critical to promoting optimum plant growth and yield while
protecting the environment. Optimum management of this resource
includes
- Handling and treating waste properly
- Testing soil and manure regularly
- Setting realistic yield goals
- Applying manure in a uniform and timely
fashion
- Practicing soil conservation and environmental
sustainability
Tables 1 and 2
show average nutrient values for four dairy manure types. Table
1 also shows the range in concentrations that make up the average.
Note the variability! Because nutrient values vary considerably over time,
it is important to have a manure sample analyzed for nutrient content
before applying the manure to the land. Because of the nature of manure
slurry systems, it may not always be possible to have a sample analyzed
before land application. However, analysis results received after the
slurry application will indicate whether there is a need for supplemental
fertilizer. Waste samples, from North Carolina, can be analyzed for $4
by the North Carolina Department of Agriculture (NCDA), Plant,
Waste and Soultion Advisory Service, 4300 Reedy Creek Road,
Raleigh, NC 27607-6465. Other qualified private laboratories
can also perform the analysis (fees vary).
|
Table
1. Nutrient Composition of Dairy Manure
|
| Manure Type |
Total Nitrogen
N |
Ammonium
NH4-N |
Phosphorus
P205 |
Potassium
K2O |
| Lot-scraped manure (lb/ton) |
10 |
3 |
6 |
9 |
| range |
(3 to 20) |
(2 to 15) |
(0.6 to 13) |
(2 to 20) |
| Liquid manure slurry (lb/1,000 gal) |
22 |
9 |
14 |
21 |
| range |
(8 to 50) |
(4 to 13) |
(0.2 to 38) |
(0.7 to 50) |
| Anaerobic lagoon sludge* (lb/1,000
gal) |
15 |
6 |
22 |
8 |
| range |
(3 to 42) |
(1 to 12) |
(2 to 64) |
(2 to 20) |
| Anaerobic lagoon liquid (lb/acre-inch) |
137 |
88 |
77 |
195 |
| range |
(17 to 268) |
(22 to 130) |
(10 to 233) |
(13 to 571) |
| Source: Biological &
Agricultural Engineering Department, North Caroiina State University,
1980 to 1990. |
| *No manure solids removed
before lagoon input. |
|
Table
2. Average Secondary and Micronutrient Content of Dairy
Manure
|
| Manure |
Ca |
Mg |
Se |
Na |
Fe |
Mn |
B |
Zn |
Cu |
Cl |
| Lot-scraped manure (lb/ton) |
5 |
2.2 |
1.7 |
1.3 |
0.9 |
0.1 |
0.01 |
0.1 |
0.02 |
3.3 |
| Liquid manure (lb/1,000 gal) |
10 |
4.8 |
3.1 |
3.2 |
1.8 |
0.2 |
0.02 |
0.2 |
0.05 |
6.1 |
| Lagoon sludge* (lb/1,000 gal) |
12 |
4-5 |
3.6 |
1.4 |
1.5 |
0.3 |
NR |
0.4 |
0.4 |
2.3 |
| Lagoon liquid (lb/acre-inch) |
69 |
35 |
25 |
48 |
12 |
1.3 |
0.15 |
2.0 |
0.3 |
67 |
| Note: Ca = Calcium,
Mg = Magnesium, Se = Selenium, Na = Sodium, Fe = Iron, Mn = Manganese,
B = Boron, Zn = Zinc, Cu = Copper, Cl = Chloride |
| NR = Not reported.
|
| Source: Biological
& Agricultural Engineering Department, North Carolina State
University. |
| *No manure solids removed
before lagoon input. |
Because the accuracy of the
analysis depends on a representative sample, take several subsamples from
different locations in the manure pile or the lagoon and mix them together
in a plastic bucket. After mixing the subsamples in the bucket, place
approximately 3/4 of a pint of the manure material in a nonmetallic, flexible
container, leaving some air space for gas expansion. If possible, refrigerate
or ice the sample, and deliver it to the lab promptly.
Samples of liquid manure slurries are more
difficult to obtain because the manure basin must be thoroughly agitated
before a representative sample can be taken. For liquid manure slurry
systems take samples as the slurry material is being pumped out of the
lagoon. The agitation caused by the removal of the slurry will provide
a representative sample. Record the analysis results to develop a representative
farm average as a guide for future slurry applications.
Land Application
Only a portion of the nutrients in dairy
manure are available immediately after application for use by the crop.
Some of the nutrients are part of the manure's organic structure and require
microbial decomposition to release them. In general, only about 50
percent of the organically bound nitrogen (N) and
70 to 80 percent of the other nutrients become available
to a crop during the year of application. With solid and slurry manures,
the remaining organically bound nitrogen can be released in subsequent
years and should be accounted for in fields where manure is applied annually.
Ammonium and urea are readily available forms
of nitrogen that are present in many manures. Both of these forms, however,
can change into ammonia, which evaporates readily. When surface-applied
manure is not incorporated for one month or longer, as much as 75
percent of the ammonia can be lost to the atmosphere. Incorporating
the manure within 48 hours reduces losses to about 25
percent; with direct soil injection all but 5 percent
of the ammonia is retained. Coefficients are used to estimate nutrient
availabilities and to account for different manure types and methods of
land application. These "availability coefficients" are multiplied
by the total nutrient concentration for each element as reported in the
manure analysis report or, if no sample was taken or no analysis is available,
they are multiplied by the average manure values listed in Table
1. The sum of these values is the nutrient concentrations available
to plants. Availability coefficients are listed in Table
3. If manure samples are sent to the NCDA Agronomic Division,
analysis results will report both total nutrient concentrations and plant-available
nutrients using these same availability coefficients.
|
Table
3. Dairy Manure First-Year Availability Coefficients
|
| Manure Type |
Injection |
Disking in within 48 hr |
Surface Spread |
Irrigation |
| |
P205
and K20 availability coefficients |
| All manure types |
0.8 |
0.8 |
0.7 |
0.7 |
| |
N availability
coefficients |
| Lot-scraped manure |
|
0.6 |
0.4 |
|
| Liquid manure slurry |
0.7 |
0.6 |
0.4 |
0.4 |
| Anaerobic lagoon liquid |
0.8 |
0.7 |
0.5 |
0.5 |
| Anaerobic lagoon sludge |
0.7 |
0.6 |
0.4 |
0.4 |
Land application rates should be based on
the nutrient requirements of the crop being grown. Manure can be applied
at a rate to supply any of the recommended nutrients. Be careful, however,
that the application rate chosen to meet one specific nutrient requirement
does not result in either excessive or inadequate application of other
nutrients that can negatively impact water quality or the crop's health.
If manure is applied to supply any nutrient other than nitrogen, apply
the amount suggested by soil-test recommendations or crop removal rates
(See Extension Service publication AG-439-16, Nutrient
Removal by Crops in North Carolina.)
Because manure usually does not contain the
optimum nutrient balance required for each field, be sure to check the
soil recommendations for each nutrient and, if necessary, supplement with
commercial fertilizer as needed. If annual applications continue to over
apply nutrients, environmental impacts can occur. Alternative management
strategies should be implemented before this occurs.
In most cases, dairy producers use manure
to supply the nitrogen requirements of their crops. Nitrogen recommendations
for various crops are listed in Table 4.
Adjust the application rate to match the yield capability of each field.
Applying more nitrogen than is required for the crop usually does not
increase yield and can potentially contribute to nitrate contamination
of groundwater and to elevated nitrate concentrations in forages. Nitrogen
recommendations given on North Carolina soil test reports are not based
on the soil sample submitted or the yield capabilities of an individual
field or farm. Soils test report recommendations reflect a wide range
of yield conditions across the state. To customize your nitrogen application
rates use the values in Table 4.
A worksheet with an example is included at the
end of this fact sheet to help you determine the amount of dairy manure
needed for different crops and fields.
|
Table
4. Suggested Nitrogen Fertilization Rates Based on Realistic
Yield Expectations
|
| Crop |
Suggested Nitrogen
Appllcatlon Rates |
| Wheat (grain) |
1.7 to 2.4 lb N/bu
|
| Barley (grain) |
1.4 to 1 6 lb N/bu
|
| Oats (grain) |
1.0 to 1.3 lb N/bu
|
| Rye (grain) |
1.7 to 2.4 lb N/bu
|
| Triticale (grain) |
1.4 to 1.6 lb N/bu
|
| Corn (grain) |
1.0 to 1.25 lb N/bu
|
| Corn (silage) |
10.0 to 12.0 lb N/ton
|
| Sorghum (grain) |
2.0 to 2.5 lb N/cwt
|
| Cotton |
0.06 to 0.12 lbN/lb
lint |
| Sorghum-sudangrass (hay1,2) |
45.0 to 55.0 lb N/dry
ton |
| Bermudagrass (hay1,2) |
40.0 to 50.0 lb N/dry
ton |
| Tall fescue (hay1,2) |
40.0 to 50.0 lb N/dry
ton |
| Orchardgrass (hay1,2) |
40.0 to 50.0 lb N/dry
ton |
| Annual ryegrass (hay1,2
) |
25.0 to 30.0 lb N/dry
ton |
| Small grain (hay1,2) |
50.0 to 60.0 lb N/dry
ton |
| Millet (hay1,2 ) |
45.0 to 55.0 lb N/dry
ton |
| Pine and hardwood trees3 |
40.0 to 60.0 lb N/acre/year
|
| 1 Annual
maintenance guidelines. |
| 2 Reduce
nitrogen rate by 25 percent when grazed oniy. |
| 3 0n trees
less than 5 feet tall, nitrogen will stimulate undergrowth competition.
|
Besides monitoring nutrients, maintain an
adequate soil pH. Optimum soil pH promotes good yields, nutrient availability,
and manure decomposition. When dairy manure is applied at agronomic rates,
high salinity (excess salt) has not been a problem, given the amounts
of rainfall normally received in North Carolina.
The most recently applied manure is not the
only source of nutrients; in most fields, some nutrients are available
from previous manure applications or previous legume crops. With the exception
of nitrogen, updated soil tests are the best means of determining nutrient
reserves from these sources. Table 5
can be used to estimate the available nitrogen carryover from legumes.
Nitrogen carryover from manure is more difficult to estimate. If manure
has been applied to a field for several years in succession, reduce the
nitrogen rate below the suggested guidelines in Table
4. Table 6 provides an estimate
of the potential nitrogen from residual carryover after 5 and 10 years
of continuous manure applications. To use these numbers effectively, you
need an estimate of the average nitrogen content of the manure and the
application rate over the period. An example is included in the following
worksheet to show how this number can be used to adjust application
rates.
|
Table
5. Estimated Residual Nitrogen Provided by a Good Stand
of Legumes Grown in Rotation
|
| Legume |
Residual Nitrogen
Available
(lb/acre) |
| Alfalfa1 |
80 to 100 |
| Harry vetch1 |
80 to 100 |
| Crimson clover1 |
60 to 75 |
| Austrian winter pea1 |
50 to 60 |
| Soybeans2 |
15 to 30 |
| Peanuts2 |
20 to 40 |
| 1
Killed before planting current spring crop. |
| 2
Legume planted in previous year. More nitrogen will be available
if the fall-planted crop immediately follows the legume. On sandy
soils and in years with normally high precipitation, less nitrogen
will be available to spring-planted crops. |
|
Table
6. Estimates of Residual Manure Nitrogen that Is Available
after 5 and 10 Years of Continuous Application
|
| Manure Type |
Years of Application |
Total Nitrogen Carryover
(%) |
| Solid |
5 |
15 |
| |
10 |
20 |
| |
| Slurry |
5 |
10 |
| |
10 |
15 |
Plant tissue analysis is another excellent
tool that you can use to fine tune manure application rates. The NCDA
also provides this service.
To minimize nitrogen losses, apply manure
as close as possible to planting time or to the stage of crop development
requiring maximum nitrogen uptake. Good timing increases the amount of
nitrogen used by the crop and thus reduces the amount of nitrate that
may leach into groundwater. Contamination of surface water and groundwater
is greater when manure is applied in the fall or early winter for spring
crops in the absence of a cover crop.
Whether dairy manure is applied with a manure
spreader or by irrigation, it is important that it be applied uniformly.
Nonuniform application leads to nutrient excesses and deficiencies, reduced
yields, and uneven crop growth.
Spreaders can apply manure at varying rates
and patterns, depending on forward travel speed, power takeoff (PTO)
speed, gear box settings, gate openings, spread widths, and overlaps.
Spreader calibration is the process of determining the combination of
settings and travel speed needed to apply manure at the desired rate and
uniformity.
Spreader
Capacity
The capacity of liquid spreaders is normally
rated by the manufacturer in gallons. Multiply the capacity in gallons
by 0.0042 to find the capacity in tons. Solid and semi-solid
spreaders are rated by the manufacturer either in bushels or cubic feet.
(Multiply bushels by 1.25 to get cubic feet.) Most spreaders
have two ratings capacities: (1) struck, or level full, and (2) heaped.
Because manures and litters have different densities, perform an on-farm
test. Fill a 5-gallon bucket level full with material to
be spread. Do not pack the material into the bucket but ensure that it
settles as it would in a loader spreader. Weigh the bucket full and then
empty. Multiply the weight of the contents by 1.5 to find the weight in
pounds per cubic feet. Multiply this value by the capacity of the spreader
in cubic feet and divide the result by 2,000 to find the
weight in tons of the material in a spreader load.
Calibration
Method 1
This method is most useful for liquid spreaders
but can be used for all types. Spread at least one full load of manure,
preferably in a square or rectangular field pattern for ease of measuring,
with normal overlaps. Measure the length and width of the area covered,
recognizing that the outer fringe areas of the coverage will receive much
lighter applications than the overlapped areas. Multiply the length by
the width and divide by 43,560 to determine the coverage
area in acres. Divide the number of tons of manure in the spreader by
the acres covered to determine the application rate in tons per
acre.
Application Rate (tons/acre) = Amount of
Manure in Spreader (tons) / [(Length Covered in Feet X Width Covered in
Feet) / 43,560]
Repeat the procedure at different speeds
and spreader settings until the desired application rate is achieved.
Calibration
Method 2
This method is often used for solid and semi-solid
spreaders. Use a tarpaulin or plastic sheet of about 100 square
feet (approximately 9 feet by 12 feet or 10
feet by 10 feet). To determine its exact surface area
multiply the tarp's length by its width. After measuring, weigh the tarp
using a set of spring-tension or platform scales, and then spread and
pin it on the field surface. Operate the spreader at its normal settings,
speed, and overlap. With a rear discharge spreader, make three passes:
the first directly over the center of the sheet and the other two on opposite
sides of the center at the normal spreader overlap spacing. Reweigh the
sheet, including the collected manure. Subtract the weight of the empty
sheet from the total weight to find the weight of the collected manure.
Multiply the weight of the collected manure in pounds by 21.8 and
divide the result by the collection area of the sheet in square feet to
find the application rate in tons per acre.
Application Rate (tons/acre) = [Amount of
Manure Collected (pounds) X 21.8] / Collection Area (square feet)
Repeat the procedure using different settings
or speeds to obtain the desired application rate.
Spreader
Pattern Uniformity
To determine the uniformity of spread and
the amount of overlap needed, evenly place (2 to 4 feet apart)
a line of small pans or trays across the spreader path. The pans should
be a minimum of 12 inches by 12 inches or 15
inches in diameter, no more than 24 inches square,
and 2 inches to 4 inches deep. Make one spreading
pass directly over the center pan. Weigh the contents caught in each pan
or pour the contents into equal-sized glass cylinders or clear plastic
tubes and compare the amount in each. Find the effective spread width
by locating the point on either side of the path center where the manure
contents caught in the containers is half of the amount collected in the
center. The distance between these points is the effective spread width.
Overlap the outer fringes of the coverage area beyond these points on
the next path to ensure a uniform application rate over the entire field.
Flat-top, pyramid, or oval patterns are most desirable and give the most
uniform rate of application. Make adjustments for unsatisfactory M, W,
steeple, or lopsided patterns.
When planning a new or expanded dairy operation,
producers need to determine if there is adequate land to properly apply
the manure. If an existing operation is expanding, it would be useful
to use the average manure nutrient analysis from the farm if records have
been maintained. When using farm records, allow for 4.1 tons
per head per year for calves, 12 tons for heifers, and 17
tons for milk cows. When records do not exist, state average figures
can be used. Table 7 has been developed
using average manure nutrient values from Table
1, availability coefficients from Table
3, and the nitrogen suggestions from Table
4.
|
Table
7. Minimum Amount of Land Needed to Apply Dairy Manure as
a Nitrogen Fertilizer Based on the Nitrogen Rate Required by
the Crop for Two Methods of Application
|
| |
Method of
Application |
Manure Handling and
Production
Units (lb N/acre/year) |
Soil
Incorporated1 |
Surface
Broadcast2 |
| |
100 |
200 |
300 |
400 |
100 |
200 |
300 |
400 |
| |
acres/animals
unit capacity |
| Lot-scraped
manure |
| Calf |
0.23 |
0.12 |
0.077 |
0.058 |
0.18 |
0.089 |
0.059 |
0.044 |
| Heifer |
0.68 |
0.34 |
0.23 |
0.17 |
0.52 |
0.26 |
0.17 |
0.13 |
| Milk cow |
0.96 |
0.48 |
0.32 |
0.24 |
0.73 |
0.37 |
0.24 |
0.18 |
| Liquid manure
slurry |
| Calf |
0.25 |
0.13 |
0.085 |
0.064 |
0.19 |
0.093 |
0.062 |
0.046 |
| Heifer |
0.75 |
0.38 |
0.25 |
0.19 |
0.55 |
0.27 |
0.18 |
0.14 |
| Milk cow |
1.1 |
0.53 |
0.35 |
0.26 |
0.76 |
0.38 |
0.25 |
0.19 |
| Anaerobic lagoon
liquid |
| Calf |
0.076 |
0.038 |
0.025 |
0.019 |
0.057 |
0.029 |
0.019 |
0.014 |
| Heifer |
0.22 |
0.11 |
0.074 |
0.055 |
0.17 |
0.084 |
0.056 |
0.042 |
| Milk cow |
0.31 |
0.16 |
0.10 |
0.078 |
0.24 |
0.12 |
0.078 |
0.059 |
| Anaerobic lagoon
sludge |
| Calf |
0.041 |
0.021 |
0.014 |
0.010 |
0.030 |
0.015 |
0.010 |
0.0075 |
| Heifer |
0.12 |
0.061 |
0.040 |
0.030 |
0.088 |
0.044 |
0.029 |
0.022 |
| Milk cow |
0.17 |
0.085 |
0.057 |
0.042 |
0.12 |
0.062 |
0.041 |
0.031 |
1Incorporated
within two days.
2Not incorporated for one month or longer; lagoon liquid
irrigated. |
To compare the economic worth of manure to
that of commercial fertilizers, convert total manure nutrient concentrations
to plant-available nutrients by using the coefficients in Table
3. For example, using the average total nutrient concentrations
of lot scraped manure from Table 1
(10 pounds of nitrogen per ton, 6 pounds of
phosphate per ton, 9 pounds of potash per ton) and the availability
coefficients for soil incorporation within 48 hours (0.6
for nitrogen and 0.8 for phosphorus and potassium),
there are 6 pounds of plant-available nitrogen, 4.8
pounds of plant-available phosphate and 7.2 pounds
of plant-available potash per ton of manure. At a value of $0.25, $0.22,
and $0.15 per pound for commercial nitrogen, phosphate, and
potash, respectively, one ton of lot-scraped manure would be worth
$3.64:
(6 X $0.25) + (4.8 X $0.22)
+ (7.2 X $ 0.15) = $3.64
This sum does not include the value of the
secondary or micronutrients that are present in manures, nor does it include
the cost of labor, transportation, or spreading costs to apply the manure.
In addition, it assumes that a soil test calls for applications of phosphorus
and potassium, when in fact many soils may already have adequate supplies.
Nutrients not needed should not be considered in assessing the financial
value of the manure.
Bill Jones is a dairy producer using a manure
basin to store his manure before applying it to land. He plans to plant
corn for silage in a field that had 10 years of continuous
manure applications, and he anticipates a yield of about 18 tons
of silage per acre. Because he applies this manure as a slurry, which
requires agitation, he decides to use the average nutrient values in Table
1 to determine the application rate. He does not plan to use
any preplant or starter fertilizer. His fields have grass borders to help
reduce erosion and the potential for nutrient and pesticide runoff. He
plans to incorporate the manure within 24 hours after application.
In the past 10 years he has applied an average of about 10,000
gallons of manure per acre. How much liquid manure slurry will he need
to apply per acre to meet the nitrogen needs of his silage crop? Will
he need to supplement his slurry application with commercial fertilizers
to meet the soil test recommendations of 50 pounds of phosphate
and 80 pounds of potash per acre, or will he have a surplus
of these nutrients? The answers to these questions are given in the worksheet
that follows. Use the same worksheet to determine the manure rates to
apply on your farm.
| Worksheet:
Determining the Nutrient Needs of Your Crop |
| |
Example |
Your Farm |
| 1. Crop
to be grown |
corn
silage |
______
|
| |
| 2. Total
nutrients required |
|
|
| a. nitrogen |
|
|
| (a1)
yield goal (tons)1 |
18 |
______ |
| (a2)
lb N/unit production (Table 4) (lb/ton) |
12 |
______ |
| (a3)
N needed (lb/acre) (2a1 x 2a2) = (18 x 12) |
216 |
______ |
| b. P2O5
(soil test) (lb/acre) |
50 |
______
|
| c. K2O (soil
test) (lb/acre) |
80 |
______
|
| |
|
|
| 3. Pounds
of starter or preplant fertilizer used |
|
|
| a. N (lb/acre) |
0 |
______
|
| b. P2O5
(lb/acre) |
0 |
______
|
| c. K2O (lb/acre) |
0 |
______
|
| |
| 4. Residual
N credit from legumes (Table 5) (lb/acre) |
0 |
______
|
| |
| 5. Net
nutrient needs of crop (lb/acre) |
|
|
Nitrogen: total need
(item 2a) minus additional N from starter (item
3a) minus N from legume (item 4)
a. N: 120 -10 - 20 (lb/acre) |
216 |
______
|
Phosphorus: total need
(item 2b, 2c) minus additional nutrients from starter
(item 3b, 3c)
b. P2O5: 50 - 34 (lb/acre) |
50 |
______
|
Potassium: total need
(item 2 b, 2c) minus additional nutrients from preplant
fertilizer (item 3b, 3c)
c. K2O: 50 - 0 (lb/acre) |
80 |
______
|
| |
|
Rate of Manure to
Apply
|
| 6. Nutrient
totals in manure (from Table 1 or waste
samples). If analysis report already gives available nutrients,
skip this item. |
|
|
| a. Total N (lb/1,000
gallons)2 |
22 |
______
|
| b. P2O5
(lb/1,000 gallons)2 |
14 |
______
|
| c. K2O (lb/1,000
gallons)2 |
21 |
______
|
| |
| 7. Nutrients available
to crop (items 6a, 6b, and 6c) times
availability coefficients (Table 3) or as reported on manure analysis
if present. |
|
|
| a. Available N: 22 x
0.6 (lb/1,000 gallons)2 |
13.2 |
______
|
| b. Available P2O5:
14 x 0.8 (lb/1,000 gallons)2 |
11.2 |
______
|
| c. Available K2O:
21 x 0.8 (lb/1,000 gallons)2 |
16.8 |
______ |
| |
| 8. Residual
N available to crop. Average application rate in past years times
average N concentration (Table 1 or from
manure analysis reports) times percent residual N (Table 6) times
availability coefficient (Table 3). If units
are are lb/1,000 gallons divide answer by 1,000.
From example:
Average rate applied = 10,000 gal/acre
Average N concentration = 22 lb/1,000 gal
(10,000 x 22 x 0.15 x 0.6)/1,000 =
|
19.8 |
______
|
| |
| 9.
Application rate to supply priority nutrient |
|
|
| a. Priority
nutrient |
Nitrogen |
______
|
| b. Amount
of priority nutrient needed (lb/acre from item 5a) |
196.2 |
______
|
c. Rate
of manure needed to supply priority nutrient (9b/7a)
multiply by 1,000 if units are lb/1,000 gal
(196.6/13.2) x 1,000 (gal/acre) = |
14,864 |
______
|
| |
|
|
| 10. Pounds
per acre of all nutrients supplied at the application rate required
to meet the needs for the priority nutrient. For each nutrient,
multiply the available nutrients (items 7a, 7b, and
7c) times manure rate (item 9c). Divide by 1,000
if units are 16/1,000 gal. |
|
|
| a. N supplied:
13.2 x 14,864/1,000 (lb/acre) |
196.2 |
______
|
| b. P2O5
supplied: 11.2 x 14,864/1,000 (lb/acre) |
166.5 |
______
|
| c. K2O
supplied: 16.8 x 14,864/1,000 (lb/acre) |
249.7 |
______
|
| |
|
|
| 11. Nutrient
balance: net nutrient need (-) or excess (+) after application
of manure at calculated rate. Amount of nutrient applied by manure
(items 10a, 10b, and 10c) minus net
amount needed by crop (items 9b, 5b, and 5c). |
|
|
| a. N balance:
196.2 - 196.2 |
0 |
______
|
| b. P2O5
balance: 166.5 - 50 |
+116.5 |
______
|
| c. K2O
balance: 249.7 - 80 |
+169.7 |
______
|
| |
| Note:
Calculation format modified from Pennsylvania Department of Environmental
Resources, Field Application of Manure, October 1986.
1 Substitute appropriate
yield units.
2 Substitute appropriate manure units.
|
|