Global Advanced Research Journal of Agricultural Science (GARJAS) ISSN: 2315-5094
March 2019 Vol. 8(3): pp. 126-137
Copyright © 2019 Global Advanced Research Journals
Full Length Research Paper
Effect of additives on greenhouse gas emissions and nitrogen losses during storage of pig manure in Vietnam
Tran Minh Tien1*, Lars Stoumann Jensen2, Vu Thi Khanh Van3, Vu Duong Quynh4, Myles Oelofse2
1 Soils and Fertilizers Research Institute; Le Van Hien Street, Duc Thang, Bac Tu Liem, Hanoi, Vietnam
2 Plant and Soil Science Lab., Dept. of Plant and Environmental Sciences, Faculty of Science, University of Copenhagen (UC-SCIENCE), Thorvaldsensvej 40, DK-1871 Frederiksberg C, Copenhagen, Denmark;
3 National Institute of Animal Sciences; Thuy Phuong, Bac TuLiem, Hanoi, Vietnam
4 Institute for Agricultural Environment, Me Tri, Nam Tu Liem, Hanoi, Vietnam
.*Corresponding Author's Email: firstname.lastname@example.org
Accepted 20 March, 2019
This study investigated the effects of three different types of additives to stored pig manure on total nitrogen andammonia (NH3) loss and greenhouse gas (GHG) emissions in Vietnam. The experiment consisted of five treatments (T1) farmer’s practices, continuous manure addition, T2 control, all manure added initially, T3 biochar amendment, T4 superphosphate amendment and T5 microbial inoculants) with three replicates of each treatment. Through the 90-day storageexperiment, no significant increase in temperature occurred in any of the treatments, indicating no active compostingtook place, possibly due to only partial aerobic conditions in the reactors. Cumulative analyses for the individual gasesCO2, CH4 and N2O indicate that GHG emissions resulting from the different treatments were not hugely different.Farmers normal practices generally had higher emissions than other practices, with losses that were significantly highestfor CO2, whilst for CH4 they were just as high as the highest emitting treatment (biochar), and for N2O the emission washighest. Overall N losses were not markedly affected by the treatments, and therefore the effects of additives arerelatively marginal, although it was clear that farmers practice of continuously adding manure without proper coverageor other elimination of loss risk will result in a manure of poorer fertilizing quality. We therefore recommend that moreexperimental work needs to be carried out, where larger volumes of manure are treated and other methods oramendments are tested, in order to find ways to efficiently reduce manure N losses and GHG emissions to theenvironment.
Keywords: Manures, Greenhouse gases, Storage, Additives
Bouwman L, Goldewijk KK, Van Der Hoek KW, Beusen AHW, Van Vuuren DP, Willems J, Rufino MC, Stehfest E (2011). Exploring global changes in nitrogen and phosphorus cycles in agriculture induced by livestock production over the 1900-2050 period. Proc Natl AcadSci U S A. 110, 20882–20887.
Cayuela ML, van Zwieten L, Singh BP, Jeffery S, Roig A, SÃ¡nchez-Monedero MA (2014). Biochar's role in mitigating soil nitrous oxide emissions: A review and meta-analysis. AgrEcosys Environ. 191, 5-16.
Chadwick D, Sommer S, Thorman R, Fangueiro D, Cardenas L, Amon B, Misselbrook T (2011). Manure management: Implications for greenhouse gas emissions. Anim Feed Sci Technol. 166-167, 514-531.
Chowdhury MA, de Neergaard A, Jensen LS (2014). Potential of aeration flow rate and bio-char addition to reduce greenhouse gas and ammonia emissions during manure composting. Chem. 97, 16-25.
Feilberg, A., Sommer SG (2013). Ammonia and Malodorous Gases: Sources and Abatement Technologies, AnimalManure Recycling:Treatment and Management. John Wiley & Sons, Ltd, pp. 153-175.
Fukumoto Y, Osada T, Hanajima D, Haga K (2003). Patterns and quantities of NH3, N2O and CH4 emissions during swine manure composting without forced aeration: effect of compost pile scale. Bioresour. Technol. 89, 109-114.
Gerber P, Steinfeld H, Henderson B, Mottet A, Opio C, Dijkman J, Falcucci A, Tempio G (2013). Tacklingclimate change through livestock - A global assessment of emissions and mitigation opportunities. Food and Agricultural Organization of the United Nations (FAO). Rome.
Hao X, Chang C, Larney FJ (2004). Carbon, nitrogen balances and greenhouse gas emission during cattle feedlot manure composting. J. Environ. Qual. 33, 37-44.
Hao X, Larney FJ, Chang C, Travis GR, Nichol CK, Bremer E (2005). The Effect of Phosphogypsum on Greenhouse Gas Emissions during Cattle Manure Composting. J. Environ. Qual. 34, 774-781.
Hoang KG, Dao LH (2008). Livestock development and environment protection (Vietnamese). Vietnamese livestock department, MARD, Hanoi, Vietnam.
Hristov AN, Oh J, Lee C, Meinen R, Montes F, Ott T, Firkins J, Rotz A, Dell C, Adesogan A, Yang W, ricarico J, Kebreab E, Waghorn G, Dirou JF, Dijkstra J, Oosting S (2013). Mitigation of greenhouse gasemissions in livestock production - A review of technical options for non CO2 emsssions. FAO, Rome.
IBM Corp (2011). IBM SPSS Statistics for Windows, Version 20.0. 2011. Armonk, NY: IBM Corp.
Jensen LS (2013). Animal Manure Residue Upgrading and Nutrient Recovery in Biofertilisers. In: Animal ManureRecycling – Treatment and Management (Eds. Sommer S.G., Christensen M.L., Schmidt T., Jesen L.S.) John Wiley & Sons, Ltd, pp. 271-294.
Kebreab E, Clark K, Wagner-Riddle C, France J (2006). Methane and nitrous oxide emissions from Canadian animal agriculture: A review. Can. J. Anim. Sci. 86, 135-157.
Lehmann J, Rillig MC, Thies J, Masiello CA, Hockaday WC, Crowley D (2011). Biochar effects on soil biota: A review. Soil Biol. Biochem. 43, 1812-1836.
Lindau CW, Bollich PK, Delaune RD, Patrick WH, Jr Law VJ (1991). Effect of urea fertilizer and environmental factors on CH4 emissions from a Louisiana, USA rice field. Plant Soil. 136, 195-203.
Maeda K, Hanajima D, Morioka R, Toyoda S, Yoshida N, Osada T (2013). Mitigation of greenhouse gas emission from the cattle manure composting process by use of a bulking agent. Soil Sci. Plant Nutr. 59, 96-106.
Petersen SO, Amon B, Gattinger A (2005). Methane Oxidation in Slurry Storage Surface Crusts. J. Environ. Qual. 34, 455-461.
Petersen SO, Andersen AJ, Eriksen J (2012). Effects of Cattle Slurry Acidification on Ammonia and Methane Evolution during Storage. J. Environ. Qual. 41, 88-94.
Petersen SO, Lind AM, Sommer SG (1998). Nitrogen and organic matter losses during storage of cattle and pig manure. J Agr Sci. 130, 69-79.
Rochette P, Eriksen-Hamel NS (2008). Chamber measurements of soil nitrous oxide flux: are absolute valuesreliable? Soil Sci. Soc. Am. J. 72, 331-342.
Sanchez-Monedero MA, Serramia¡ N, Civantos CGO, FernÃ¡ndez-Hernandez A, Roig A (2010). Greenhouse gas emissions during composting of two-phase olive mill wastes with different agroindustrial by-products. Chem. 81, 18-25.
Schulte EE, Hopkins BG (1996). Estimation of Soil Organic Matter by Weight Loss-On-Ignition. In: Soil OrganicMatter: Analysis and Interpretation (Editors: Magdoff, F. R.; Tabatabai, M. A.; Hanlon, E. A.). Soil Science Society of America. p. 21–31.
Smith KA, Conen F (2004). Measurement of trace gases: I. Gas analysis, chamber methods, and related procedures.Soil and Environmental Analysis: Modern Instrumental Techniques. 3rd Ed. Marcel Dekker, New York. Measurement of Trace Gases: I. Gas Analysis, Chamber Methods, and Related Procedures 433-437.
Sommer SG, Clough TJ, Chadwick D, Petersen, S.r.O., 2013. Greenhouse Gas Emissions from Animal Manure an Technologies for Their Reduction, Animal Manure Recycling: Treatment and Management. John Wiley & Sons, Ltd, pp. 177-194.
Sommer SG, Møller HB (2000). Emission of greenhouse gases during composting of deep litter from pig production: effect of straw content. J Agr Sci. 134, 327-335.
Steiner C, Das KC, Melear N, Lakly D (2010). Reducing Nitrogen Loss during Poultry Litter Composting Using Biochar. J. Environ. Qual. 39, 1236-1242
Steinfeld H, WassenaarT (2007). The Role of Livestock Production in Carbon and Nitrogen Cycles. Annu. Rev. Environ. Resourc. 32, 271-294.
TranMT, VU T.K.V., SOMMER SG, JENSEN LS (2011). Nitrogen turnover and loss during storage of slurry and composting of solid manure under typical Vietnamese farming conditions. J Agr Sci. 149, 285-296.
Tran MT, Bui HH, Luxhoi J, Jensen LS (2012). Application rate and composting method affect the immediate and residual manure fertilizer value in a maize-rice-rice-maize cropping sequence on a degraded soil in northern Vietnam. Soil Sci. Plant Nutr. 58, 206-223.
Vu Q, Tran T, Nguyen P, Vu C, Vu V, Jensen L (2012). Effect of biogas technology on nutrient flows for small-and medium-scale pig farms in Vietnam. NutrCyclAgroecosyst. 94, 1-13.
Vu QD, de Neergaard A, Tran TD, Hoang HTT, Vu VTK, Jensen LS (2015). Greenhouse gas emissions from passive composting of manure and digestate with crop residues and biochar on small-scale livestock farms in Vietnam. Environ. Technol.36, 2924-2935.
Wang J, Duan C, Ji Y, Sun Y (2010). Methane emissions during storage of different treatments from cattle manure in Tianjin. J Environ Sci. 22, 1564-1569.
Webb J, Sommer S, Kupper T, Groenestein K, Hutchings N, Eurich-Menden B, Rodhe L, Misselbrook T, Amon B (2012). “Emissions of Ammonia, Nitrous Oxide and Methane During the Management of Solid Manures," In Agroecology and Strategies for Climate Change, (Ed: E. Lichtfouse), Springer Netherlands, pp. 67-107.
Yamulki S (2006). Effect of straw addition on nitrous oxide and methane emissions from stored farmyard manures. AgrEcosys Environ. 112, 140-145.
- Tran Minh Tien on Google Scholar
- Tran Minh Tien on Pubmed
- Lars Stoumann Jensen on Google Scholar
- Lars Stoumann Jensen on Pubmed
- Vu Thi Khanh Van on Google Scholar
- Vu Thi Khanh Van on Pubmed
- Vu Duong Quynh on Google Scholar
- Vu Duong Quynh on Pubmed
- Myles Oelofse on Google Scholar
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