Abstract

This paper is modified from a manuscript published under CC BY license (Chen et al., 2021b; doi: 10.20944/preprints2021105.0210.v1) <b><sc>Abstract.</sc></b> The risk of inhalation exposure to elevated concentrations of hydrogen sulfide (H<sub>2</sub>S) and ammonia (NH<sub>3</sub>) during the agitation of stored swine manure is high. Once or twice a year, farmers agitate manure before pump-out and application to fields. Agitation of the swine manure causes the short-term releases of highly toxic levels of H<sub>2</sub>S and NH<sub>3</sub>. In our previous pilot-scale studies, the biochar powder had shown significant mitigation of H<sub>2</sub>S and NH<sub>3 </sub>emissions when surficially applied to manure immediately before agitation. However, fine biochar powder application poses hazards by itself and may not be practical to apply on a farm scale, especially when livestock and workers are present. We hypothesized that applying pelletized biochar to manure surface is just as effective as applying powder to protect farmers and animals from excessive exposure to H<sub>2</sub>S and NH<sub>3</sub>. This work reports on the lab-scale proof-of-the-concept trials with biochar pellets on the lab-scale. The objective was to compare the biochar pellets and biochar powder on their effectiveness of mitigation on H<sub>2</sub>S and NH<sub>3</sub> gases during 3-hour long swine manure agitation. Three scenarios were compared in (n=3) trials (i) control, (ii) 12.5 mm thick surficial application to manure surface of biochar powder, and (iii) an equivalent (by mass) dose of pelletized biochar applied to manure surface. The biochar powder was bound with 35% (wt) water into ~5 x 10 mm (dia x length) pellets. Biochar powder was significantly (p<0.05) more effective than the biochar pellets. Still, pellets reduced total H<sub>2</sub>S and NH<sub>3</sub> emissions by ~72% and ~68%, respectively (p=0.001), compared with ~99% by powder (p=0.001). The maximum H<sub>2</sub>S & NH<sub>3 </sub>concentrations were reduced from 48.1±4.8 ppm & 1,810±850 ppm to 20.8±2.95 ppm & 775±182 ppm by pellets, and to 22.1±16.9 ppm & 40.3±57 ppm by powder, respectively. These reductions are equivalent to reducing the maximum concentrations of H<sub>2</sub>S and NH<sub>3</sub> during the 3-h manure agitation by 57% and 57% (pellets) and 54% and 98% (powder), respectively. Treated manure properties hinted at improved nitrogen retention, yet not significant due to high variability. We recommend scaling-up and trials on the farm-scales using biochar pellets to assess the feasibility of application to large manure surfaces and techno-economic evaluation.

Highlights

  • Animal production provides an excellent source of fertilizer in the form of manure for crop production

  • Pellets reduced total H2S and NH3 emissions by ~72% and ~68%, respectively (p=0.001), compared with ~99% by powder (p=0.001)

  • The maximum H2S & NH3 concentrations were reduced from 48.1±4.8 ppm & 1,810±850 ppm to 20.8±2.95 ppm & 775±182 ppm by pellets, and to 22.1±16.9 ppm & 40.3±57 ppm by powder, respectively

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Summary

Introduction

Animal production provides an excellent source of fertilizer in the form of manure for crop production. The animal-production system's sustainability depends on the efficient carbon (C) and nitrogen (N) cycling between manure, crops, and animal feed. Swine manure is generated and stored year-round. Manure can be utilized by crops seasonally, typically before seed planting and/or after the harvest. Stored manure requires pump-out and emptying to make room for a continued farm operation. Shortterm (hours) agitation of manure is required to stir up and incorporate settled solids into a slurry that pumps can handle. Manure agitation is facilitated by using a high-capacity pump with recirculation for a vigorous mechanical stirring of settled manure solids at the bottom of the storage pit

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