Poultry litter can provide a significant supply of nutrients for crop production in areas of Kansas where a supply of litter is available (Figure 1). Although Kansas is not a major producer of poultry, there is an abundant supply of litter from the nearby states of Arkansas, Missouri, and Oklahoma, which rank among the largest producers of poultry in the U.S. The acreage available to receive poultry litter has been declining in Arkansas, Missouri, and Oklahoma in recent years because of environmental concerns and nutrient management regulations. Thus, litter availability in areas such as southeast Kansas has been on the rise.
Figure 1. Poultry litter. Photo by Dan Donnert, K-State Research and Extension.
Poultry litter should serve as an excellent complement to commercial nitrogen (N) fertilizers. Phosphorus (P) content in poultry litter is usually high, and application rates should be based on P levels to avoid potential surface water contamination.
Moisture content and nutrient concentration in poultry litter can be highly variable and depend mainly upon production conditions, storage, and handling methods. Therefore, laboratory analysis is the best way to determine the level of N and P in the material to be applied. Average values for the different types of poultry manure collected over a period of time are shown in Table 1. Actual laboratory analysis of 213 poultry manure samples from southeast Kansas is shown in Figure 2. There is a large range in nutrient values, likely due to the source of the litter. However, a good sample average to expect would be 56-53-46 (N-P-K).
Table 1. Types and nutrient content of poultry litter
|
|
Typical moisture content |
|
||
|
N |
P2O5 |
K2O |
||
|
Layer |
High |
35 |
40 |
20 |
|
Pullet |
Low |
40 |
45 |
40 |
|
Breeder |
High |
40 |
60 |
40 |
|
Turkey |
Low |
60 |
60 |
55 |
|
Broiler |
Low |
60 |
60 |
55 |
Figure 2. Results of analysis of 213 samples of poultry manure from southeast Kansas. Sources: K-State Research and Extension.
For maximum efficiency of manure use, it is essential to know the nutrient content of the manure. A laboratory analysis should be done on the poultry litter before applying it to land. A laboratory analysis provides information regarding nutrient levels, as well as the chemical forms of these nutrients. This information is necessary for an adequate estimation of nutrient availability and application rates.
For more information, see K State Extension publication MF-2562, “Estimating Manure Nutrient Availability,” at: http://www.ksre.ksu.edu/bookstore/pubs/MF2562.pdf
Nitrogen availability
What is the crop availability of N shortly following poultry litter application?
In the case of N, it is important to consider that this nutrient is primarily in the organic form in poultry litter (up to 75-80% organic N). Organic N needs to be mineralized before becoming available to crops. A fraction of this organic N may become part of the soil organic matter pool and unavailable to crops in the short term.
Field and laboratory studies suggest the fraction of total nitrogen that becomes plant available the first year of application is approximately 45-55%, which includes both the inorganic N in the manure and a percentage of the organic N. This value varies depending upon components in the litter and the method of handling and application. For example, poultry litter that contains a large fraction of bedding material will tend to have lower N availability in the year of application. Reduction in N availability may also occur when litter is aged and has undergone some composting. Nitrogen lost from the volatile ammonium fraction at the time of application on the soil surface can also reduce plant available N. Ammonium volatilization is typically higher during windy and warm days. Incorporation of litter immediately after application will reduce volatilization and potential nutrient loss by water runoff in case of a rainfall event, in addition to reducing the odor of the litter.
If the manure is applied to pastures, the percentage of N utilized by the forage in the first year will depend on whether the pasture consists of cool-season or warm-season grasses. For cool-season grasses, such as fescue pasture, N utilization will likely be less than 50% in the first year. Most of the growth in cool-season pasture occurs early in the year. The microbial community will not mineralize as much N early in the spring as later in the summer. Fall applications may result in better N utilization for fescue than winter or spring applications. For warm-season grasses, such as bermudagrass pasture, nitrogen utilization from manure will likely be close to 50%. In both cases, producers should base application rates on the P and K needs of the grass and supplement additional N fertilizer to meet the N needs of the grass.
Phosphorus and potassium availability
When manure is applied to the soil, what percentage of the phosphorus and potassium is available to the crop during the first year?
A large fraction of the P in manure is considered to be plant-available immediately after application. The fraction that is not plant available shortly after application will become available over time.
Estimated values of P availability are from 50 to 100%. This range accounts for variation in sampling and analysis and for P requirements with different soil test levels. Use the lower end of the range of P availability values (50%) for soils testing “Very Low” and “Low” (below 20 ppm). In these situations, large yield loss could occur if insufficient P is applied and soil P buildup is desirable.
On the other hand, use 100% availability when manure is applied to maintain soil test P in the “Optimum” soil test category and when the probability of a yield response is small.
Several studies have shown that manure P is a valuable resource that is comparable to inorganic fertilizer P for crop production. These two P sources are similarly effective when the manure P concentration is known, and the manure is applied properly. Nevertheless, excessive application of manure P (e.g., at rates sufficient to meet the crop’s N needs) often results in excessive soil P buildup, resulting in a higher risk of surface water contamination.
This problem of excessive P buildup in the long term can be minimized by:
- Applying manure to meet the P needs of the crop and using inorganic sources of fertilizer to complement nitrogen needs,
- Constantly monitoring soil test P levels, and
- Using the P-index to assess the potential impact of P buildup on water quality.
Producers should consider actual P application rates and not just tons per acre of manure being applied. Uniform application of manure at precise rates can also be difficult. Careful calibration of manure applicators is needed. If these aspects are not considered, the efficiency of manure P compared with inorganic fertilizer P may be reduced. Careful management pays off.
Availability of potassium is usually near 100% with proper application. Poultry litter can also provide significant amounts of secondary and micronutrients.
Peter Tomlinson, Environmental Quality Specialist
ptomlin@ksu.edu
Dorivar Ruiz Diaz, Nutrient Management Specialist
ruizdiaz@ksu.edu