Impact of Repeated Applications of Liquid Swine Manure and Biogas Production By-Products on Soils and Crops
Rates of raw liquid swine manure or biodigestate of 3,000 to 4,000 gallons per acre – around 75 to 100lbs of nitrogen per acre per year – provided optimum yields of barley, report J.J. Schoenau and T.N. King of the University of Saskatchewan and S.S. Malhi of Agriculture and Agri-Food Canada. Their paper is published in the 2011 Annual Report from the Prairie Swine Centre.
Summary
Short and long-term application of fresh and processed liquid swine manure to Saskatchewan soils at agronomic rates of nutrients that balance crop removal over time contribute to significant yield and protein benefits in the crop while minimizing nutrient loading and risk of escape to soils and water.
Introduction
In the spring of 2007, a new experiment was set up near Dixon,
Saskatchewan to look at crop response to swine manure biodigestate
that is produced from biogas production, in comparison to
conventional liquid swine manure and urea fertilizer. Three rates
of digestate and liquid hog manure (1,500, 3,000 and 6,000 gallons
per acre) were applied along with three rates of urea: 50, 100 and
200 lbs N/acre.
On long-term (since 1997) swine manure monitoring
experiments at Dixon, 15 treatments of liquid swine manure
were applied by the Prairie Agricultural Machinery Institute
(PAMI), continuing the sequence applied for the previous 10 years.
At the Melfort long-term liquid swine manure injection site, five
treatments involving different rates and sequences of liquid swine
manure were applied, with and without sulphur fertilizer, as in the previous seven years.
Assessments of grain and straw yield, nutrient
concentrations, soil nutrients and properties were made on plant and
soil samples collected every fall in 2007, 2008 and 2009 to determine
how manure applications affected crop growth and soil properties.
Results and Discussion
* "Rates of raw liquid swine manure or biodigestate of 3,000-4,000 gallons (around 75-100 lbs N) per acre per year provided optimum yields" |
Crop yield
Significant yield responses to swine manure application were observed
in 2007. An example of crop response to swine manure treatments
is shown for the Melfort study site (Figure 1). At the Dixon site,
there appeared to be little difference in behaviour of the manure digestate
compared to the conventional liquid manure in terms of yield
responses observed. Annual applications of around 3,000 gallons per acre,
62-89 N/acre (around 34,000 litres per hectare; 70-100kg total N per hectare) as liquid hog
manure and biodigestate resulted in maximum yield at all sites.
This supports the concept that rates of addition of liquid swine manure in
the order of 3,000–4,000 gallons per acre per year is the 'agronomic
or 1X rate'. Higher rates of application (6,000 gallons per acre or 2X) made in the
previous year showed good carry-over into the next year. In 2007, the
highest rates of application (4X agronomic rate) generally had reduced
yield compared to the 2X and 1X rates.

In 2008, a strong yield response of canola to manure application was
noted at all sites. Annual applications of swine manure at 2X and 4X
rates tended to produce the highest yields, likely reflecting better
growing conditions than in 2007 and also the greater nutrient requirements
of canola as compared to the oats and barley
grown at the sites in 2007. Application at the 4X rate
(13,200 gallons per acre) every year results in excessive soil nitrate
levels. As in previous years, there was no difference in
agronomic effect of the biodigestate liquid swine manure
compared to the raw liquid manure. As well, the
addition of the nitrification inhibitor to liquid swine
manure had no significant effect on yield. Injection of
liquid swine manure produced superior yields compared
to broadcast and incorporation. Liquid swine manure
appears to supply close to sufficient amounts of phosphorus
and sulphur, as response of the liquid manure
treatments to supplemental phosphorus and sulphur was muted in 2008.
In 2009, close to maximum yield of oat was obtained
at rates of around 3,000 gallons per acre of raw liquid swine manure and biodigestate. As in previous years, there appeared to be little difference
in the agronomic performance of biodigestate from manure
biogas production versus raw liquid swine manure when considered
on a 'per kg of nutrient added' basis. At the long-term liquid swine
manure trial, the barley yield was maximized at the 4X annual rate,
reflecting good growing conditions and high yield potential at the
site. Consistent with results of previous years there was no response
to addition of supplemental phosphorus fertilizer on the swine manure plots,
and no response to addition of nitrification inhibitor.
Treatments with
skipped applications of nutrient the two previous years did not yield
as high when manure was added in 2009. It appears that rates of
addition of approximately 100kg liquid swine manure - N/ha 90lb
N/ac (around 3,000-5,000 gallons per acre per year) will maximize production
over time in these soils without creating issues of nutrient loading.
The results at Melfort long-term swine trial support this, as near
maximum yield was observed at these rates. Application at double
1X rate every second year (6,000–10,000 gallons per acre every second year)
did not result in as high an oat yield in the second year, 2009, pointing
towards lower efficiency of total nutrient recovery in the 'double-
up' approach. Some benefit was observed from the commercial sulphur
fertilizer application treatment made in 2008. In the 2009 oat crop,
it showed up in the urea treatments and also in the high rate liquid
manure treatment and only for the elemental sulphur form. Generally, it
appears that some benefit may be observed from fertilization with
supplemental fertilizer sulphur on liquid swine manured soils but the variability
in effects regarding crop, form and rates in which benefits are
observed makes the benefits difficult to predict.
Soils
Generally, available nitrogen levels in the soil in the fall after harvest increased
with increasing rate of liquid swine manure. Salinity was not
significantly affected except at the 4X (13,200 gallons per acre) annual application
rate at the Dixon long-term site where, for example in 2008, it
was elevated to 2.2mS per cm and in 2009, it was elevated to 1.3mS per cm.
Repeated application of liquid swine manure at these high rates may
create potential salinity concerns for crop growth, and also resulted in
greatly elevated nitrate (>200kg per hectare; 178lb per acre) in the 0-30cm and
30-60cm depths, as did the 4X rate of urea. The content of nitrate in
the 60-90cm and 90-120 cm depths was assessed in the Dixon long-term
site in the fall of 2009 and revealed that only the 4X annual application
of swine manure and urea had elevated concentrations of
nitrate at these depths, with 60-100kg nitrate-nitrogen (NO3-N) present in each depth
increment compared to less than 10kg per hectare for the rest of the treatments.
The 1X liquid swine manure rate (around 3,000-4,000 gallons per acre) does not
result in soil nitrate or phosphate loading.
Accumulation of soil extractable phosphorus was not evident in either the raw
liquid hog manure treatments or the biodigestate after three years
of application. Reflecting the low phosphorus content of the liquid swine manure
source used at the long-term site, soil extractable phosphorus levels were
relatively unaffected by liquid manure application. The broadcast and
incorporation treatment at Dixon had significantly lower nitrate than
injected, again supporting that along with lower crop nitrogen recovery, nitrogen
losses from the system are greater with broadcast and incorporate
versus injection.
The application of swine manure either on a long-term or short-term
basis did not affect soil organic carbon or soil sodicity values to any
great extent but there was a trend to higher organic carbon corresponding
with manure application. A long period of animal manure
application seems necessary to produce significant increases in soil organic
carbon in these soils. Manure application tended to increase soil
strength slightly but not significantly in the long-term manure trials.
The application of swine manure either on a long-term or short-term
basis did not affect soil organic carbon or soil sodicity values to any
great extent, but there was a trend to higher organic carbon corresponding
with manure application. A long period of animal manure
application seems necessary to produce significant increases in soil organic
carbon in these soils. Manure application tended to increase soil
strength slightly but not significantly in the long-term manure trials.
Conclusion
Rates of raw liquid swine manure or biodigestate of 3,000-4,000 gallons
per acre per year (around 75-100lbs nitrogen per acre per year) gave optimum yields
of the oats and canola grown over the three years and did not result
in excessive soil nutrient loading.
As anticipated, application of swine
manure at these rates over three years had little impact on soil properties
like pH, salinity and organic carbon compared to the urea fertilized
treatments and the unfertilized control.
In the long-term (more than 10 years), liquid swine manure trials, application rates of 3,000–4,000 gallons
per acre every year (around 75–100lbs nitrogen per acre per year) gave near-optimal
yields for the crops examined (oats, canola, barley) and were not associated
with any loading of nitrate or phosphate in the soil.
As such,
these rates of application are again confirmed as the 'agronomic' optimum.
Double these rates applied every second year also gave good
yield response in the year of application, and provided significant residual
benefits in the second year after application. However, especially
in the moister environment encountered at Melfort, yields in the
second year following application were not equivalent to the annual
application rate, suggesting that larger applications intended to carry
through for subsequent years may not be as efficient.
High rates of
liquid swine manure applied annually re 2X (around 6,600 gallons per acre) and especially
4X (13,200 gallons per acre) often did not produce significant yield benefit
above the 1X rate and lead to accumulation of excessive quantities of
nitrate in the soil profile (0-60cm) and beneath.
Furthermore, 4X rates
of liquid swine manure and urea increased soil salinity slightly. Owing
to the relatively low phosphorus content of the liquid swine manure
used in this study, levels of soil test extractable phosphorus were only elevated
significantly in the 4X rates.
Acknowledgements
Strategic funding provided by Saskatchewan Agriculture Development Fund and Sask Pork.
August 2012