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Manitoba Agriculture, Food and Rural Initiatives

PROJECT RESULTS

 

Effect of Hog Manure Applications on Weed Control Management

 

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Applicant: 

Dr. Annemieke Farenhorst

Department of Soil Science

University of Manitoba

Winnipeg, Manitoba  R3T 2N2  Canada

 

Table of Contents:

 

ARDI Project:

 

#00-458

Total Approved: $53,647
Date Approved: August 20, 2001

Project Status:

Completed April, 2004

 

Background and Objective:

In order to benefit from hog manure applications, producers should have access to information on the effects of manure on weed pressures and herbicide performance.  Therefore, the objective of this study was to quantify the effect of liquid hog manure applications to agricultural land on weed emergence and densities and on herbicide efficacy and carry over risks.

This objective was met.

Procedure and Project Activities:

This study focused on the herbicide trifluralin and had both a field and laboratory component.  The field component was designed to quantify the effect of manure applications and synthetic fertilizers on weed emergence and densities; and on herbicide efficacy and carry over risks.  The field trials were conducted on three different soil types: a fine sandy loam, a loam, and a clay soil.  For each soil type treatment, the field experiment was a randomized block design with five nitrogen treatments and four replicates per treatment.  The manure and urea fertilizer treatments were applied in 2001.  Following these applications Treflan EC (trifluralin) treatment was applied at a recommended field rate of 0.93 L/acre.  Canola was grown on all plots.  In 2002, all plots received an equal amount of synthetic fertilizers and were seeded to oats, a crop that is sensitive to trifluralin residues in soil.  As such, the oat crop served as a bioassay to compare the level of crop injury among fertilizer treatments and soil type.  The amount of trifluralin in soil in 2001 and 2002 was also quantified by chemical analysis.  Weed emergence and growth was measured in 2001, 2002 and 2003.

This study also included a laboratory component that further examined the impact of manure management on trifluralin persistence in soil.  Ms. M. Reimer, a graduate student whose stipend was supported, in part by ARDI, conducted these laboratory studies.  Ms. Reimer made greater progress than initially projected.  This allowed us to conduct additional laboratory studies with available resources.  It was decided to select two additional herbicides: glyphosate and 2,4-D.  Since there was some impact of manure applications on herbicide persistence in soil, Ms. M. Reimer also conducted studies that helped to explain the reasons for these observed differences in herbicide persistence.

Both herbicide mineralization and sorption were measured.  Herbicide mineralization refers to the transformation of a herbicide into carbon dioxide. This transformation process is the result of microorganisms in the soil.  When herbicide mineralization is high, the herbicide product is less persistent in soil.  Herbicide sorption refers to the retention of herbicides in soil.  When the sorption is high, herbicides are strongly retained by soil and are less available for plant uptake.  Herbicides that are bound by soil are also less likely to be degraded by microorganisms in soil.

Results and Discussion:

Results indicated that there were a total of 11 different weed species present across the fertilizer and soil type treatments in the three years.  The most prominent weed species were volunteer canola, volunteer wheat, dandelions and wild oats.  Both soil type and fertilizer treatment were significant factors in influencing total weed densities.  The fine sandy loam had much lesser weed infestations than the clay and loam soils.  Also, plots that had received twice the recommended rate of manure, based on soil N, demonstrated greater weed infestations relative to other treatments.  The application of high rates of urea also resulted in larger weed infestations.  The effect of soil type on weed densities was most pronounced for dandelions.  The effect of fertilizer treatment on weed densities was particularly significant for wild oats in 2003. 

The amount of trifluralin in soil decreased during the growing season, but there were no significant trifluralin losses from soil during the winter months. As such, the potential for trifluralin carry-over and crop injury risks can be assessed at the end of the growing season in the year that herbicides are applied.  A similar trend in herbicide persistence over time has been observed for the products Odyssey (imazethapyr and imazamox) and Pursuit (imazethapyr) in Manitoba soils.  The amount of trifluralin present in soil in 2002 was sufficiently high to cause crop injury to oats at the 3 to 6 leaf stage.  Despite similar levels of trifluralin in soil (based on chemical extractions), the loam soil demonstrated lesser visual signs of oat injury at the 3 to 6 leaf stage than the clay and fine sandy loam soils.  This suggested that soil type has an influence on the bioavailability of trifluralin to plants.  There was no effect of fertilizer treatment on the amount of oat injury caused by trifluralin residues in soil.

Oat yields in 2002 were greater for the fine sandy loam soil than for the clay and loam soils because there was less weed competition in the fine sandy loam soil.  Thus, crop injury induced by trifluralin early in the growing season had a lesser effect on oat yield than weed density.  Oat yields were also better in the soils that received either manure or urea in 2001, relative to soils than received no fertilizers in the first year of study.

Results of the laboratory experiments indicated that the effects of fresh manure application and long-term manure applications on trifluralin and glyphosate persistence in soil, varied by soil type.  This suggests that trifluralin and glyphosate persistence in soil is influenced by factors other than manure applications.  Long-term (10 to 40 years) manure applications to agricultural land decreased the persistence of trifluralin and glyphosate in some soils, perhaps due to better soil tilth induced by manure amendments.  The effect of fresh manure applications on trifluralin persistence in soil was influenced by the timing between manure and herbicide application. When trifluralin was applied soon after manure applications, trifluralin persistence in soil was decreased.  When the time between manure and herbicide application was delayed, trifluralin persistence in soil was increased.

The effect of fresh manure applications on herbicide persistence was more pronounced for 2,4-D than for glyphosate and trifluralin.  The persistence of 2,4-D increased with increasing applications of fresh manure to soil.  The greatest effects of fresh manure applications on 2,4-D persistence in soil were observed when the herbicide was applied at 7 to 28 days after manure applications, as compared to herbicide and manure applications at the same time.

There was no impact of manure on soil microbial activity in soil, but there was some indication that manure influenced the amount of herbicides sorbed by soil.  Fresh manure application to soil increased trifluralin sorption in only one soil type which, when amended with fresh manure, also showed greater trifluralin persistence in soil.  The sorption of 2,4-D was also enhanced in soils that received high rates of fresh manure, thereby explaining the observed increases of 2,4-D persistence in soils amended with fresh manure.  A history of manure applications onto agricultural land decreased trifluralin sorption in soil, contributed to the lesser persistence of trifluralin in some fields with a history of manure applications.  It is possible that long-term manure applications alter soil organic matter characteristics, therefore altering the degree of trifluralin sorption by soil.  Either fresh or long-term manure applications had no effect on glyphosate sorption by soil.  Glyphosate is strongly sorbed onto mineral soil particles such as clay so that soil organic matter characteristics are generally less important to glyphosate retention in soils.

Conclusions:

This study suggests that high nutrient applications to agricultural land could encourage an increase in weed densities for some species.  Specifically, the application of twice the recommended rate of manure based on soil N increased wild oat densities in agricultural land.  It was also clear that trifluralin is persistent in Manitoba soils and can cause injury to sensitive crops such as oats.  The level of visual injury to oats at the 3 to 6 leaves stage was less pronounced for loam soils than fine sandy loam and clay soils.  However, oat yields were more influenced by density of weeds in plots that the level of trifluralin residues in soil.

It is clear that manure applications had no influence on trifluralin persistence and carry-over in the field experiment.  However, the results of the laboratory experiments provided some indication that long-term (10 to 40 years) manure applications to agricultural land decreased trifluralin and glyphosate persistence in some soils, perhaps due to better soil tilth induced by manure amendments.  The effect of manure on herbicide persistence in soil varied with soil characteristics and is expected to be also dependent on land management practices other than manure.  Fresh manure applications to soil had a greater and more consistent effect on 2,4-D persistence than on trifluralin and glyphosate persistence.  The persistence of 2,4-D in soil decreased with increasing manure application rates.  There was evidence that the effect of manure on trifluralin and 2,4-D persistence in soil was due to the effect of manure on herbicide sorption in soil and, hence, the availability of the herbicide to microorganisms that degrade herbicide in soil. Manure did not influence the activity of microorganisms in soil.

Acknowledgements:

We gratefully acknowledge the funding that was provided for this research by the Canola Council of Canada and the Agri-Food Research and Development Initiative.  This work was also supported by other agencies, including the Natural Sciences and Engineering Research Council support to students, and in-kind contributions from technical support at the Carman Research Station, University of Manitoba.

 

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