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Research questions posed
What researchers
found
What researchers did not
find
More about the P-Index
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ISU
researchers experiment with deep-banding
phosphorus at an ISU research farm. The
multi-year project also involved 8 farmeR
cooperators.
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Iowa livestock producers have been keeping a
watchful eye on government regulators this year as they
develop rules for future manure management in the state. Of
particular interest has been the Phosphorus Index, or P
Index, and how it will be used to determine application
rates in producers’ manure management plans.
Developed by scientists from Iowa State University, the USDA
National Soil Tilth Laboratory and the USDA Natural
Resources Conservation Service, the P Index estimates the
risk of phosphorus loss from a field. Research has shown
phosphorus that moves from farm fields and into water bodies
can cause algae blooms and other water quality problems.
The index, released in 2001, uses several factors to
calculate a site-vulnerability ranking that includes
erosion, soil P tests, farmer management practices and
location of the field. The ranking is then used to determine
how manure can be applied to fields, at what rates, and
whether applications are based on nitrogen (N) or phosphorus
(P) content.
Even with the advent of this management tool, there are
still many unresolved questions about the role and movement
of phosphorus in the soil. Leopold Center-funded work has
both informed the development of the P Index and tried to
identify soil P thresholds.
In the most recently completed Leopold Center project,
members of the ISU Departments of Agronomy and Agricultural
and Biosystems Engineering examined the relationships of P
to crops, soils and water. Experiments were designed to
compare different application methods, placement methods,
and types of P tests (agronomic and environmental) to each
other, to yields and to P loss.
Research questions posed
Some of the questions going into this work included:
• How is soil P affected by fertilizer or manure
applications?
• Can variable rate application help manage soil P?
• What are the relationships between environmental P and
runoff or tile flow?
• What’s the threshold value for soil P and how can farmers
use it to manage P?
Several field experiments were conducted over three years,
some on ISU research farms and some on private farms. Five
long-term trials evaluated the effects of P application
methods (deep banding, injecting, broadcast) on crop yield
and soil P for no-till and chisel-disk tillage systems.
Three long-term on-farm trials assessed the value of
variable-rate application of fertilizer and liquid swine
manure to achieve better P distribution over the area of the
field.
Three other long-term trials evaluated the impact of
fertilizer and manure P applications of total and dissolved
P loss through tile drainage and surface runoff. Soil
phosphorus was measured using routine agronomic tests that
are considered appropriate for soils in the region, and also
with what are called ‘environmental’ tests.
The commonly used agronomic tests emphasize evaluation of
plant-available P. The environmental tests focus on
leachable and mobile P and bioavailable (algae-available) P.
Investigators thought the environmental tests would provide
a better assessment of phosphorus that would move into water
supplies, rather than plant-available P.
What researchers found
Current guidelines for soil phosphorus levels, measured in
parts per million (ppm), are on a scale of Very Low, Low,
Optimum, High and Very High. Although farmers may have an
‘optimum’ test result, they may add P over the recommended
rate to help manage risk and to assure higher yields. This
research, however, confirmed a very low probability of corn
and soybean yield response at soil test P levels higher than
16 ppm.
The research also found that placement of phosphorus is
important, even though it has little or no effect on grain
yield. In this project, deep banding or injecting P greatly
reduced the accumulation of P at or near the soil surface
when compared with applications to no-till soils or soils
managed with chisel-disk tillage. Further, incorporating P
by injection significantly reduced both dissolved P and
total P loss. This makes sense because P at the soil surface
tends to move more easily off the land in rainfall events.
Farmers have questioned potential yield gains or risk that
might be associated with using fertilizer P versus using
liquid swine manure as a source of P. In this work, using
variable application, there were seldom significant yield
increases when the researchers compared variable rate
applications of P fertilizer with variable rate applications
of P-based liquid swine manure.
However, the variable-rate method itself managed the P
application much better, that is, less P is applied to the
fields overall and within-field soil-test P variability is
always reduced. This is important for overall cost of P
application, and for more sustainable and environmentally
sound P management.
What researchers did not find
Researchers looked for a relationship between P
concentrations in tile drainage and soil test P
Generally, P losses in tile drainage rose with increasing P
application rates and with the amount of soil-test P in the
surface soil. However, the actual concentration in tile
drainage in the test sites was low, and could not be
significantly related to the soil-test P until these levels
exceeded 80 to 100 ppm, which is four to five times higher
than the optimum levels for crops. Even then, the drainage
concentrations were quite low. The environmental P soil
tests proved no more useful in identifying a specific
relationship than the common agronomic tests.
One objective of this work was to determine a threshold – a
turning point to trigger specific increases in P loss for
specific amounts of soil test P. Researchers looked for a
clear threshold where soil surface and total loss would
dramatically increase or decrease given specific soil test
levels, even those that were two and four times above the
recommended levels.
That elusive relationship was not identified by this work.
Additionally, it was hoped that environmental P tests might
be more useful than common agronomic soil tests to establish
relationships between soil-test P and P concentration in
surface runoff. No findings could confirm any relationship.
Overall the work was useful in validating the Iowa P index
as an all-purpose tool for statewide farmer use. It
reinforced some management issues and provided new insights
into others.
It may, however, not go as far as possible in achieving the
site-specific sustainability that would contribute even
further to improved statewide P management. Lead researcher
Antonio Mallarino said there may be other models that would
allow farmers to further tailor agronomic and environmental
P management practices to their own lands, and he is
committed to make these other options a reality for farmers.
More about the P Index
More than 150 people attended five public hearings in March
conducted by the Iowa Department of Natural Resources to
gather comments about proposed rules regarding phosphorus
and manure management plans. The proposed rules and a fact
sheet on the use of the P Index are available at the Iowa
DNR web site at:
www.state.ia.us/epd/watewtr/feedlot/feedlt.htm,
or on the Iowa NRCS web site at:
www.ia.nrcs.usda.gov/
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