Combination of Borax and Quebracho Condensed Tannins Treatment to Reduce Hydrogen Sulfide, Ammonia and Greenhouse Gas Emissions from Stored Swine Manure

Waste to Worth: Spreading science and solutions logoWaste to Worth home | More proceedings….

Abstract

Livestock producers are acutely aware for the need to reduce gaseous emissions from stored livestock waste and have been trying to identify new technologies to address the chronic problem.  Besides the malodor issue, toxic gases emitted from stored livestock manure, especially hydrogen sulfide (H2S) and ammonia (NH3) are environmental and health hazards for humans and animals and under scrutiny by the Environmental Protection Agency for regulatory control of concentrated animal farm operations (CAFOs). 

These odorous and toxic gases are produced by bacteria during the fermentation of the stored manure.  Sulfate reducing bacteria convert sulfate (SO4) to sulfide (H2S) during the fermentation.  During storage of swine manure, about 60% of NH3 nitrogen is also loss.  If NH3 loss can be prevented, the fertilizer value of swine manure would improve and reduce the need for additional commercial nitrogen fertilizer.

There are very few technologies available to reduce H2S, NH3 and greenhouse gas emissions from stored livestock manure, which meet the criteria of being: inexpensive, safe for farmers and animals, and environmentally sustainable. Previous research has shown that borax and quebracho condensed tannin are effective in inhibiting H2S production in stored swine manure. The present research demonstrates that a combination of borax and quebracho condensed tannin is highly effective in reducing all gaseous emissions (H2S, NH3, CO2, CO, N2O and CH4) and in retaining more nitrogen in swine manure. Lesser amounts of borax and quebracho condensed tannin are needed when combined to achieve a similar reduction in H2S production to using much larger amounts of either product alone. 

Phytotoxicity studies show that the level of tolerance of crops to borax-tannin combination treated swine manure is:  alfalfa > corn > wheat > soybean >> dry beans.  Quebracho condensed tannin does not appear to be toxic to crops.

Why Study Tannins?

Develop methods for reducing emissions from stored swine manure.

What Did We Do?

Tested the effects of addition of combinantions of borax and quebracho condensed tannins to swine manure slurries on  production of gaseous emissions and more retaining nitrogen in the manure.

What Have We Learned?

Addition of various combinations of borax and quebracho condensed tannins to swine manure slurries was highly effective in reducing all gaseous emissions (H2S, NH3, CO2, CO, N2O, and CH4) and in retaining more nitrogen in swine manure.  Lesser amounts of borax and tannin are needed when combined to achieve  a similar reduction in H2S production to using much larger amounts of either product alone.   Phytotoxicity studies show that the level of tolerance of crops to borax-tannin combination treated swine manure is:  alfalfa > corn > wheat > soybean >> dry beans. 

Future Plans

We are interested in transferring this research to on-farm sites.

Authors

Melvin Yokoyama, Professor, Dept. of Animal Science, Michigan State University, E. Lansing, MI 48824, yokoyama@msu.edu

Terence R. Whitehead, Research Microbiologist, USDA-ARS-National Center for Agricultural Utilization Research, Peoria, IL 61604

Cheryl Spence, USDA-ARS-National Center for Agricultural Utilization Research, Peoria, IL 61604

Michael A. Cotta, USDA-ARS-National Center for Agricultural Utilization Research, Peoria, IL 61604

Donald Penner, Dept. of Crops and Soil Sciences, Michigan State University, E. Lansing, MI 48824

Susan Hengemuehle, Dept. of Animal Science, Michigan State University, E. Lansing, MI 48824

Janis  Michael, Dept. of Crops and Soil Sciences, Michigan State University, E. Lansing, MI 48824

Additional Information

Whitehead, T.R., Spence, C., and Cotta, M.A.  Inhibition of Hydrogen Sulfide, Methane and Total Gas Production and Sulfate-Reducing Bacteria in In Vitro Swine Manure Slurries by Tannins, with Focus on Condensed Quebracho Tannins. (2012) Appl. Microbiol. Biotech. http://link.springer.com/article/10.1007/s00253-012-4562-6/fulltext.html

Development and Comparison of SYBR Green Quantitative Real-Time PCR Assays for Detection and Enumeration of Sulfate-Reducing Bacteria in Stored Swine Manure.  (2008) J. Appl. Microbiol. 105: 2143-2152.  http://onlinelibrary.wiley.com/doi/10.1111/j.1365-2672.2008.03900.x/pdf

USDA-ARS-NCAUR Bioenergy Research Unit Home Page: http://ars.usda.gov/main/site_main.htm?modecode=36-20-61-00

 

The authors are solely responsible for the content of these proceedings. The technical information does not necessarily reflect the official position of the sponsoring agencies or institutions represented by planning committee members, and inclusion and distribution herein does not constitute an endorsement of views expressed by the same. Printed materials included herein are not refereed publications. Citations should appear as follows. EXAMPLE: Authors. 2013. Title of presentation. Waste to Worth: Spreading Science and Solutions. Denver, CO. April 1-5, 2013. URL of this page. Accessed on: today’s date.

Greenhouse Gas Emissions From Land Applied Swine Manure: Development of Method Based on Static Flux Chambers

Waste to Worth: Spreading science and solutions logoWaste to Worth home | More proceedings….

Abstract

A new method was used at the Ag 450 Farm Iowa State University (41.98N, 93.65W) from October 24, 2012 through December 14, 2012 to assess GHG emission from land-applied swine manure on crop land. Gas samples were collected daily from four static flux chambers.  Gas method detection limits were 1.99 ppm, 170 ppb, and 20.7 ppb for CO2, CH4 and N2O, respectively.  Measured gas concentrations were used to estimate flux using four different models, i.e., (1) linear regression, (2) non-linear regression, (3) non-equilibrium, and (4) revised Hutchinson & Mosier (HMR). Sixteen days of baseline measurements (before manure application) were followed by manure application with deep injection (at 41.2 m3/ha), and thirty seven days of measurements after manure application.  

Static flux chamber (pictured) method was developed to measure greenhouse gas emissions from land-applied swine manure from a corn-on-corn system in central Iowa in the Fall of 2012.  Gas samples were collected in vials and transported to the Air Quality Laboratory at Iowa State University campus. 

Why Study Greenhouse Gases and Land Application of Swine Manure?

Assessment of greenhouse gas (GHG) emissions from land-applied swine manure is needed for improved process-based modeling of nitrogen and carbon cycles in animal-crop production systems.

What Did We Do?

We developed novel method for measurement and estimation of greenhouse gas (CO2, CH4, N2O) flux (mass/area/time) from land-applied swine manure. New method is based on gas emissions collection with static flux chambers (surface coverage area of 0.134 m^2 and a head space volume of 7 L) and gas analysis with a GC-FID-ECD.

Baseline (post tilling) greenhouse gas (GHGs) emissions monitoring was followed with swine manure application in the Fall of 2012 (pictured) and about 10 weeks of post-application monitoring of GHGs.

New method is also applicable to measure fluxes of GHGs from area sources involving crops and soils, agricultural waste management, municipal, and industrial waste.  New method was used at the Ag 450 Farm Iowa State Univeristy (41.98 N, 93.65 W) from October 24, 2012 through December 14, 2012 to assess GHG emission from land-applied swine manure on crop (corn on corn) land. Gas samples were collected daily from four static flux chambers. Gas method detection limits were 1.99 ppm, 170 ppb, and 20.7 ppb for CO2, CH4, and N2O, respectively.

What Have We Learned?

Measured gas concentrations were used to estimate flux using four different mathematical models, i.e., (1) linear regression, (2) non-linear regression, (3) non-equilibrium, and (4) revised Hutchinson & Mosier (HMR). Sixteen days of baseline measurements (before manure application) were followed by manure application with deep injection (at 41.2 m3/ha), and thirty seven days of measurements after manure application.   Preliminary net cumulative flux estimates ranged from 115,000 to 462,000 g/ha of CO2, -4.65 to 204 g/ha of CH4, and 860 to 2,720 g/ha N2O.  These ranges are consistent with those reported in literature for similar climatic conditions and manure application method.

Greenhouse gases (GHGs) were analyzed in the Air Quality Laboratory (ISU) using dedicated GHGs gas chromatograph.  The picture above shows an example of gas sample analysis for CO2, GH4 and N2O.  Each ‘peak’ represents one of the tagget GHGs.  Gas concentrations were used in a mathematical model to estimate GHG flux (mass emitted/area/time).

Future Plans

Spring 2013 measurements of GHG flux from land-applied swine manure are planned.  The spring study will follow the protocols developed for the Fall 2012 season.  Estimates of the Spring and Fall GHG flux will be used to develop GHG emission factors for emissions from swine manure in Midwestern corn-on-corn systems.  Emission factors will be compared with literature data.

Authors

Dr. Jacek Koziel, Associate Professor, Iowa State University Department of Agricultural and Biosystems Engineering koziel@iastate.edu

Devin Maurer, Research Associate, Iowa State University Department of Agricultural and Biosystems Engineering

Kelsey Bruning, Undergraduate Research Assistant, Iowa State University Department of Civil, Construction and Environmental Engineering

Tanner Lewis, Undergraduate Research Assistant, Iowa State University Department of Agricultural and Biosystems Engineering

Danica Tamaye, Undergraduate Research Assistant, University of Hawaii College of Agriculture, Forestry, and Natural Resource Management

William Salas, Applied Geosolutions

Acknowledgements

We would like to thank the National Pork Board for supporting this research.

 

The authors are solely responsible for the content of these proceedings. The technical information does not necessarily reflect the official position of the sponsoring agencies or institutions represented by planning committee members, and inclusion and distribution herein does not constitute an endorsement of views expressed by the same. Printed materials included herein are not refereed publications. Citations should appear as follows. EXAMPLE: Authors. 2013. Title of presentation. Waste to Worth: Spreading Science and Solutions. Denver, CO. April 1-5, 2013. URL of this page. Accessed on: today’s date.