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Author: Manitoba - Agriculture and Food
Introduction
Depending on the type of manure and how it is stored and applied, the nitrogen
and phosphorus in manure may supply crop needs for an entire growing season. In
addition to these nutrients, manure contains potash, several trace elements and
large amounts of organic matter. Organic matter from manure can increase the organic
matter content of the soil which can improve the water holding capacity, aeration,
infiltration, soil tilth, biological quality and resistance to erosion.
Like any fertilizer, a proper application rate must be calculated to ensure
optimum agronomic and economic benefit. This information is calculated using
manure analysis information and should be monitored by soil testing where manure
has been applied.
Nutrient Availability
Nutrients in manure exist in two forms: organic and inorganic. Since only inorganic
forms of nitrogen and phosphorus are available to plants, only a portion of
the total nutrients can be utilized in the year of application. The organic
forms must first be converted to an inorganic form (mineralized) which occurs
naturally in the soil. This can be advantageous for the crop because not all
of the nutrients from manure are immediately available. The slow release of
nutrients minimizes possible crop damage and prevents excess nutrients from
being lost before plant uptake occurs.
Availability of manure nutrients to the crop depends on the organic/inorganic
makeup of the manure. Approximately 50% of the total phosphorus in manure is
in the organic form, with only a small portion available to plants in the year
of application. The remaining 50% of the total phosphorus is inorganic phosphorus,
similar to commercial fertilizer. In general, 50% of the total phosphorus in
manure is available to plants in the first year. To ensure enough phosphorus
is available to a growing crop, add 12-15 lbs/ac of P2O5 as a starter fertilizer
with the seed. Check the fertilizer recommendations of specific crops for any
seed placed fertilizer restrictions.
With nitrogen, three different measurements are given in a manure analysis:
- Total Kjeldahl Nitrogen (TKN) is the total amount of organic and ammonia
nitrogen in the sample.
- Ammonia nitrogen (NH3) is the amount of inorganic nitrogen that is readily
converted to plant available forms.
- Organic nitrogen is determined by the difference between total nitrogen
and ammonia nitrogen.
The general rule of thumb for nitrogen mineralization from manure is to expect
25-30% of the organic nitrogen to be available to plants in the first year,
with the remainder becoming available during the next three years at a decreasing
rate. Soil testing should be conducted to confirm the actual amount of available
nitrogen in any specific situation. When considering application rates of manure
based on nitrogen content, consider the amount of readily available nitrogen
(ammonia) relative to the amount of gradually available organic nitrogen. In
some cases, it may be necessary to add a starter fertilizer to ensure the crop
has enough nutrients available during its early growth stages.
Volatilization of ammonia represents a significant means of nitrogen loss.
Loss of ammonia depends upon method of application and time prior to incorporation,
as shown below:
Method of Application
|
% N Loss (incorporation within 3 days)
|
| *broadcast,
no incorp. |
25-35 |
| broadcast,
immediate incorp. |
15-25 |
| broadcast,
no incorp. on established forage |
35 |
| injection |
0-2 |
| *irrigation |
25-35 |
| *If time to incorporation
is greater than three days, nitrogen losses can be 40-60% for broadcasting
and 60-80% for irrigation. |
Application Methods
There are many variations of application techniques for manure. Application methods
are evaluated based on cost, level of soil disturbance, level of nutrient loss,
and odour.
Application Method
|
Advantages
|
Disadvantages
|
Broadcasting applications
-without incorporation |
relatively inexpensive |
results
in considerable odour production; intensive field traffic with manure spreaders
results in soil compaction; nutrient loss due to ammonia volatilization
and runoff |
|
-with incorporation |
incorporate
as soon as possible to reduce nutrient losses and minimize odour |
| Irrigation |
can
be applied over wet soil conditions; relatively inexpensive; should be incorporated
immediately |
nutrient
losses and odour production are higher than with other application methods |
| Direct injection
of manure into the soil |
nutrients directly placed
in root zone; results in little or no nutrient loss and minimal odour production;
may be accomplished using a liquid manure spreader equipped with a cultivator-type
injection unit or pumped directly from a storage facility to a field up
to two miles away using pipes and hoses connected to an injector equipped
with sweep openers |
these
types of injectors result in high soil disturbance, making them unacceptable
units in perennial forage or zero tillage fields; cost, time, fuel and labour
are limiting factors |
Overall Strategy
To have an effective manure management strategy, all of the following considerations
must be integrated into a program that accounts for the nutrients in manure
and manages the nutrients to satisfy crop needs.
- manure analysis - field and laboratory methods of analysis are available.
Field test kits allow for immediate analysis of nitrogen content and should
be checked against a laboratory analysis first. Manure analysis from a given
operation should change very little from year to year if there are no major
changes in feed ration or manure storage. Manure from sampling lagoons may
vary greatly if not thoroughly agitated, since solids usually settle out
during storage.
- sufficient land base - do you own enough land close by or do pre-arrangements
need to be made with a neighbor?
- soil test - according to Farm Practices Guidelines.
- methods of application - if not applying manure by direct injection,
incorporate manure as soon as possible to avoid losses due to runoff and
volatilization losses and to reduce odour.
- time of application - apply as close to planting as possible to minimize
risk of nutrients lost to runoff, volatilization, leaching, etc. (Winter
manure application is not recommended because a large amount of the manure
may be lost as runoff and poses risks to surface water pollution).
- calculate application rate - based on nutrient that will be present in
the soil in the largest quantity (nitrogen or phosphorus). Once a fertilizer
application rate has been calculated, determine the size of land base needed
to apply the available manure at the calculated rate.
The following tables serve as guidelines to calculate an application rate
for manure. Keep in mind the principle of fertilizing according to crop
needs and the nitrate guidelines for soil.
A. Moisture Use & Root Penetration
|
| Crop |
Annual Water Use (in.) |
Root
Penetration (ft.) |
| alfalfa |
20 |
14 |
| sainfoin |
16 |
11 |
| Russian wild ryegrass |
13 |
7 |
| tall wheatgrass |
12 |
7 |
| sweetclover |
11 |
7 |
| barley & wheat |
7 |
4 |
B. How Much Manure Nitrogen to Apply
- General Guidelines
|
|
Crop
|
N (lb/ac) |
| alfalfa |
225 |
| grasses |
150 |
| alfalfa-grass
mixtures |
175 |
annual
crops:
-medium to heavy soils
-light soils |
80
60 |
Note to points 6A and 6B:
These are not absolute values; there is a trade-off between over- and under-fertilizing
with manure. Over-fertilizing to meet or slightly surpass crop nitrogen
requirements so that no additional fertilizer need be applied is valid,
but excess nitrate in the soil must be closely monitored. Under-fertilizing
requires multiple fertilizer applications, which increases costs and the
risk of excess nitrates in the soil from a subsequent application. A general
recommendation would be to fertilize as close to crop requirements as possible,
so that few nitrates are present only in close proximity to the soil surface
after the growing season. |
- calibrate equipment - make sure the application equipment is applying
manure at the target rate.
- uniform application
- keep plans and records
Conclusion
Treat livestock manure as a fertilizer. Once its nutrient content is determined,
manure can be managed to benefit crop production with minimal risk to soil and
groundwater contamination. The two key managmement points to remember are:
- Soil Test
- Manure Analysis
Sample Application Rate Calculation Based
on Manure Analysis:
A liquid hog manure sample is analyzed to have 27.3 lb/1000 gal of TKN, 19.7
lb/1000 gal of ammonia and 8.1 lb/1000 gal of phoshorus. Based on soil test
and crop requirements, the producer wishes to apply at a rate that meets all
of his nitrogen requirements, which is 90 lbs/ac. Phosphate requirements are
25 lb/ac. The manure is to be broadcast in the spring followed by incorporation
one day later.
Assume:
- 15% volatilization loss (see above)
- 30% organic nitrogen available in 1st year
- 50% (approx.) total phosphorus available in 1st year
|
MANURE APPLICATION
RATE
Calculation Worksheet - Example
|
| Step
1. Soil Test Data |
|
Field
ID: SE
quarter |
| Nutrient |
Target Rate(lb/ac to
add) |
| Nitrogen |
90 |
| Phosphate |
25 |
| Step
2. Data from Manure Analysis |
|
Nutrients |
Units (lb/1000 gal or
kg/1000L): |
| Total
Nitrogen (A) |
27.3 |
| Ammonia
(B) |
19.7 |
| Organic
Nitrogen (A-B) |
7.6
(C) |
| Phosphorous
(D) |
8.1 |
| Phosphate (D×2.3) |
18.6
(E) |
| Step
3. Amount of manure nitrogen available to crop |
|
Volatilization
losses due to application equipment |
15%
(F) |
| Organic
nitrogen available in first year (C×0.3) |
2.3
(G) |
| Ammonia
available (B×[100-F]%) |
16.7
(H) |
| Total
Nitrogen available in growing season (G+H) |
19.0
(I) |
| Step
4. Application rate based on nitrogen requirements |
|
Nitrogen
Target Rate ÷ (I) = Application Rate (J)
90 lb/ac ÷ 19.0 lb × 1000 gal = 4737 gal/ac ---->
apply 4500-5000 gal/ac
|
| Step
5. Amount of manure phosphate available to crop |
|
Phosphorus
availability factor |
50%
(K) |
| Total
available phosphate (E×K) |
9.3
(L) |
Compare
(L) with Phosphate Target Rate:
9.3 lb/1000 gal ----> 46.5 lb/4600 gal;
46.5 lb/ac ÷ 25 lb/ac = 1.9 × (acceptable) |
|
MANURE APPLICATION
RATE
Calculation
Worksheet
|
| Step
1. Soil Test Data |
|
Field
ID: |
| Nutrient |
Target Rate(lb/ac to
add) |
| Nitrogen |
|
| Phosphate |
|
| Step
2. Data from Manure Analysis |
|
Nutrients |
Units (lb/1000 gal or
kg/1000L): |
| Total
Nitrogen (A) |
|
| Ammonia
(B) |
|
| Organic
Nitrogen (A-B) |
(C)
|
| Phosphorous
(D) |
|
| Phosphate
(D×2.3) |
(E)
|
| Step
3. Amount of manure nitrogen available to crop |
|
Volatilization
losses due to application equipment |
%
(F) |
| Organic
nitrogen available in first year (C×0.3) |
(G)
|
| Ammonia
available (B×[100-F]%) |
(H)
|
| Total
Nitrogen available in growing season (G+H) |
(I)
|
| Step
4. Application rate based on nitrogen requirements |
|
Nitrogen
Target Rate ÷ (I) = Application Rate (J) |
|
| Step
5. Amount of manure phosphate available to crop |
|
Phosphorus
availability factor |
50%
(K) |
| Total
available phosphate (E×K) |
(L) |
Compare
(L) with Phosphate Target Rate:
- if
(L) is less than the target rate: add a starter phosphate fertilizer
- if
(L) is greater than the target rate: do not exceed the target
rate by more than 2.5×; otherwise, calculate an application rate based
on phosphate instead of nitrogen (switch steps 3 and 5).
|
|
| |