
Spring
2003
Crop
and soil response to liquid swine manure application
by
John E. Sawyer, Antonio P. Mallarino, and John Lundvall, Department of
Agronomy
In this
article, we summarize partial results from a project that has been demonstrating
crop utilization of liquid swine manure nutrients - from understanding
the nutrient application rate to measuring crop response. General goals
and details of methods such as manure sampling, analyses, and application
rates being used were outlined in two previous issues of the Odor and
Nutrient Management newsletter (Fall 2002
and Winter 2002 issues). Herein,
we present results for crop response to applied manure nitrogen (N). The
final article in this series, planned for the Summer 2003 newsletter,
will summarize crop response to applied manure phosphorus (P). For the
first 3 years of the project (2000-2002), we worked with 16 producer cooperators
at 39 production/field sites located in 12 counties.

Harvesting replicated
strip trails in the swine manure utilization project.
Corn response to manure N application.
Low- and high-rate (the target rate at most sites was 75 and 150 lb total
manure N/acre for corn rotated with soybean, and 100 and 200 lb total
manure N/acre for continuous corn) liquid swine manure applications substantially
increased average corn strip yields relative to the no manure check at
15 of 17 evaluation sites in 2000–2002 where manure was applied
before the corn crop (Table 1). Of the total yield increase from manure
application, the majority typically came with the low manure rate (average
27 bu/acre strip yield increase across sites with the low manure rate
and an average additional 10 bu/acre increase with the high rate). At
several sites, the low rate seemed to supply adequate plant-available
N, because there was no additional yield response with the high rate.
Two sites in 2000 (Hardin and Plymouth) were nonresponsive due to high
manure application history or drought conditions. Strip yield increases
were considered mainly due to manure-N at most sites, although part of
the strip yield increases could be due to response to manure P or potassium
(K) at some sites when soil tests were optimum or lower. When warm, drying
conditions during broadcast application (Clay 2001) or excessively wet
spring conditions (Washington 2001, Davis 2002, Washington 2002) resulted
in apparent N losses, or where corn followed corn, then corn yield was
increased with higher manure rates (Table 1). If yield was increased with
the higher manure rate, it was due to a combination of specific manure-N
rates applied and site conditions (corn N requirement and potential N
loss). These results with liquid swine manure, and potential effects from
loss conditions, are similar to those encountered with N fertilizer.

Cooperator Rob Stout during August 27, 2003, field day held at his farm.

Corn yield response to additional N fertilizer was most
consistent in the strips that received no manure or the low manure rate.
In 2000 and 2001, at only the most N-responsive sites did corn yield increase
with additional fertilizer-N applied in addition to the half-rate manure
application, and with only up to 40 lb fertilizer N/acre (Figure 1). At
those field sites receiving excess rainfall after manure application (denitrification/leaching
losses) or warm temperatures at manure application (N volatilization losses
of surface applied manure) corn yield increased with additional fertilizer-N
applied in addition to the high manure rate - no sites in 2000, one site
in 2001, and two sites in 2002. These 3 years of yield data suggest that
supplementing swine manure with additional fertilizer N is only necessary
when the manure-N rate is inadequate to meet specific corn needs or losses
reduce N supply. Corn yield response to fertilizer N in the residual manure
year (manure applied before soybean and then corn grown the following
year) was similar for all prior year manure rates (Table 2), indicating
no second year crop-available manure N supply.

Figure 1. Effect
of average liquid swine manure total-N rate (five corn rotated with soybean
sites in 2000 and 2001) and additional fertilizer-N on corn grain yield,
relative corn ear leaf SPAD chlorophyll meter reading, and cornstalk nitrate-N
concentration.
Grain yield and relative leaf greenness indicated similar
corn responsiveness to manure and fertilizer N (Figure 1 for five similar
C-S rotation sites). Leaf greenness (Minolta SPAD chlorophyll meter readings)
will not indicate excess N but will show deficiency (at approximately
<95 percent relative SPAD - relative to adequately N fertilized corn
greenness); therefore, those readings do not increase once maximum greenness
is reached, even with more N. Corn yield responded to higher manure or
fertilizer N rates when relative SPAD values were below 95 percent. Relative
SPAD values above 95 percent generally indicated yield did not increase
with more N. When manure N or manure plus fertilizer N application was
greater than corn need (especially when the rate was excessive), stalk
nitrate tests indicated high levels (well above 2,000 ppm). The average
manure total-N rate of approximately 150 lb N/acre seemed to supply adequate
plant-available N at these five sites. At an average 80 lb total manure
N, approximately 40 lb additional N/acre was needed from fertilizer.

Corn was very responsive to liquid swine manure application,
with large yield increases at responsive sites. Most yield increase was
with the low manure
rates, with further yield increase from high manure rates at the more
N responsive sites. It was possible to meet corn N requirements solely
with liquid swine manure. Although it is not possible to exactly discern
first year crop availability, yield and plant N measurements suggest that
N in liquid swine manure is highly available to corn in the year of application
and seems to support the current recommendation that first year swine
manure N availability is near 100 percent. The Winter 2002 newsletter
article noted that the average ammonium-N in liquid swine manure samples
collected at application was 83 percent of the total-N, indicating that
crop availability should be high. Results from these 3 years also indicate
that liquid swine manure should be applied following steps of known manure
total N content (manure preapplication and at application laboratory analysis
instead of book values); applied with equipment calibrated at rates to
supply corn N fertilization recommendations; applied in a manner to minimize
volatile loss (injection instead of broadcast); and applied at times to
minimize conversion of manure ammonium to nitrate well before crop use.
Summary.
The project is documenting the importance and value of liquid swine manure
as a nutrient source for crop production in Iowa. Following a comprehensive
approach of preapplication manure sampling and laboratory analyses, manure
sampling during application, and calibrated rate applications, it is feasible
to agronomically provide crop N nutrient needs from liquid swine manure.
Results from these 3 years also confirm that best management of liquid
swine manure should consider practices that enhance achieving desired
manure rates for providing N, minimize potential for N loss, and closely
estimate rates of needed N.
The ISU Swine Manure Nutrient Utilization Project,
part of the Integrated Farm/Livestock Management (IFLM) Demonstration
Program, receives funding from the Iowa Department of Agriculture and
Land Stewardship, Division of Soil Conservation, USDA Natural Resources
Conservation Service, and the Leopold Center for Sustainable Agriculture.
This is the third in a series of newsletter articles
highlighting the ISU Swine Manure Nutrient Utilization Project. The final
article will appear in the July 2003 ONM newsletter and will highlight
crop yield response to manure phosphorus application.
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