Effects of manure land application on soil properties based on multiyear state-wide data in Missouri

Purpose

Soil health is crucial for sustainable crop production, which can differ from conventional soil nutrient considerations. Analyzing a multiyear, state-wide dataset can greatly improve the understanding of soil health status. In collaboration with the Missouri N340 cover crop cost-share program, this research compiled multiyear soil sample results from fields throughout Missouri and assessed the effects of manure application strategies on soil properties.

What Did We Do?

A total of 14,473 soil samples were collected from 2015 to 2022 across Missouri. The physicochemical properties of soil samples were analyzed by the University Soil Health Assessment Center (SHAC). To evaluate the impacts of manure application, results were first compared with fields that received inorganic fertilizer, followed by the interaction with soil texture. The effects of manure type and their application method were further studied in this research.

What Have We Learned?

In most years, manure application increased potentially mineralizable nitrogen (PMN), Bray-1 phosphorus (P), permanganate-oxidizable carbon (POXC), and organic carbon, showing more significant differences in some years compared to inorganic fertilizer. There was no improvement in effective cation exchange capacity (ECEC), but aggregate stability was highly variable for manure application (Figure 1).

Figure 1: Effects of manure land application on soil properties for soil samples of 2015-2022 (M- Manure, IF- Inorganic fertilizer; significant codes: *** : < 0.001, ** : < 0.01, * : <0.05)
Figure 1: Effects of manure land application on soil properties for soil samples of 2015-2022 (M- Manure, IF- Inorganic fertilizer; significant codes: *** : < 0.001, ** : < 0.01, * : <0.05)

The interaction between manure and soil texture significantly (p<0.01) affected PMN, ECEC, organic carbon, and POXC, but no significant difference in aggregate stability was observed. There was also a significant effect of manure type on ECEC and organic carbon, as shown in Figure 2. The organic carbon of fields that received cattle and swine manure was significantly higher (p<0.05) than poultry manure-receiving fields, but there was no significant difference between cattle and swine manure.

Figure 2: Effects of manure types on soil physicochemical properties (Data are presented as mean with standard error, bars with different letters denote significantly different at p<0.05)
Figure 2: Effects of manure types on soil physicochemical properties (Data are presented as mean with standard error, bars with different letters denote significantly different at p<0.05)

In Missouri, surface application is the most commonly used application method, followed by incorporation and injection. Figure 3 illustrates the effects of different manure application methods on soil properties. There was no significant difference in PMN and Bray-1 P across the application methods. However, the application method significantly affected ECEC and organic carbon, which were higher for manure injection. Surprisingly, the aggregate stability was the lowest for fields with manure injection.

Figure 3: Effects of manure application methods on soil properties (Data are presented as mean with standard error, bars with different letters denote significantly different at p<0.05)
Figure 3: Effects of manure application methods on soil properties (Data are presented as mean with standard error, bars with different letters denote significantly different at p<0.05)

Future Plans

Data from management practices reveals notable variations in manure types and application rates across the state. Additionally, many farms have adopted cover crop practices and mixed tillage methods, including no-till, reduced tillage, and conventional tillage. Given the diversity of agricultural practices in Missouri, data collection and analysis are ongoing, with a field experiment at a university farm currently underway to provide further insights and validation.

Authors

Presenting author

Manobendro Sarker, Graduate student, University of Missouri, Columbia

Corresponding author

Teng-Teeh Lim, Extension Professor, University of Missouri, Columbia, limt@missouri.edu

Additional authors

Morgan Davis, Assistant Professor, University of Missouri, Columbia

Donna Brandt, Lead Research Specialist, Soil Health Assessment Center, University of Missouri, Columbia

Timothy Reinbott, Director, Field Operations, Agricultural Experiment Station

University of Missouri, Columbia

Additional Information

Please email us at limt@missouri.edu (Teng-Teeh Lim) or ms59d@umsystem.edu (Manobendro Sarker).

Acknowledgements

We gratefully acknowledge the Missouri Department of Natural Resources, Soil and Water Conservation Program for funding the project. We also thank Moh Moh Thant Zin, Rana Das, and Ravi Mishra from our research group for their assistance with field operations.

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