Abstract
Manure management is considered to be a main key for mitigating gas emissions from livestock buildings. Since there are a number of limitations that make it difficult to identify these conditions in farm-scale experiments, these experiments should be conducted on a laboratory scale. Therefore, the aim of this study was to develop pilot reactors for simulating the operation conditions to be used later in a farm-scale experiment. The developed reactors were made from polyvinylchloride with 1.5 m height and 0.16 m diameter to be filled with 0.19 L slurry. The generated concentrations of NH3, N2O and CH4 from the slurry were continuously analysed at 800 mL min−1 air flow rate using three different sampling methods. The concentration gradient was also analysed within gas chamber height above the slurry. No differences were apparent neither between the various sampling methods nor concentrations gradient in the gas chamber. Acid pilot reactor was developed to determine the required acid concentration and quantity. Influences of pH slurry and air flow rates on gases concentrations were investigated. At 0.32 \({\text{m}}_{\text{air}}^{3} \;{\text{m}}_{\text{slurry}}^{ - 3} \;{\text{h}}^{ - 1}\) flow rate, the reproducible value of the emissions was minimized. The emissions of NH3, N2O and CH4 were 3.2, 2.3 and 38 \({\text{mg}}\;{\text{m}}_{\text{slurry}}^{ - 3} \;{\text{h}}^{ - 1}\), respectively. In order to achieve minimum gas emissions under aerobic conditions, slurry pH should be kept in the neutral range. A comparison of gas emissions under aerobic and anaerobic conditions was conducted. Approximately 70% less NH3 and 130% more N2O were produced under aerobic than with anaerobic conditions.
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Aguirre-Villegas HA, Larson RA (2017) Evaluating greenhouse gas emissions from dairy manure management practices using survey data and lifecycle tools. J Clean Prod 143:169–179. https://doi.org/10.1016/j.jclepro.2016.12.133
Amon B, Kryvoruchko V, Amon T, Zechmeister-Boltenstern S (2006) Methane, nitrous oxide and ammonia emissions during storage and after application of dairy cattle slurry and influence of slurry treatment. Agric Ecosyst Environ 112:153–162. https://doi.org/10.1016/j.agee.2005.08.030
Amon B, Kryvoruchko V, Fröhlich M, Amon T, Pöllinger A, Mösenbacher I, Hausleitner A (2007) Ammonia and greenhouse gas emissions from a straw flow system for fattening pigs: housing and manure storage. Livest Sci 112:199–207. https://doi.org/10.1016/j.livsci.2007.09.003
Balssen E (1981) Separierung und Belüftung von Schweineflüssigmist. Dissertation, VDI 61, Kiel University, Germany
Béline F, Martinez J (2002) Nitrogen transformations during biological aerobic treatment of pig slurry: effect of intermittent aeration on nitrous oxide emissions. Bioresour Technol 83(3):225–228
Calvet S, Campelo JC, Estells F, Perles A, Mercado R, Serrano JJ (2014) Suitability evaluation of multipoint simultaneous CO2 sampling wireless sensors for livestock buildings. Sensors 14(6):10479–10496. https://doi.org/10.3390/s140610479
Calvet S, Hunt J, Misselbrook TH (2017) Low frequency aeration of pig slurry affects slurry characteristics and emissions of greenhouse gases and ammonia. Biosyst Eng 159:121–132
Cortus EL, Lemay SP, Barber EM, Hill GA (2009) Modelling ammonia emission from swine slurry based on chemical and physical properties of the slurry. Can Biosyst Eng 51:9–22
FAO (2018) FAOSTAT database. Food and Agriculture Organization, Rome. Accessible http://faostat.fao.org/site/573/DesktopDefault.aspx?PageID=573#ancor
Frosch W (2004) Experimentelle Untersuchungen zum Einsatz von Flüssigmist-Additiven zur Emissionsminderung umweltrelevanter Gase und Verbesserung der Fließeigenschaften des Flüssigmistes–dargestellt am Beispiel der Ferkelaufzucht–Habilitation, Halle
Guiziou F, Béline F (2005) In situ measurement of ammonia and greenhouse gas emissions from broiler houses in France. Bioresour Technol 96:203–207
Hahne J (2006) Abluftreinigung für Tierhaltungsanlagen, KTBL-Schrift 451. KTBL-Verlag, Darmstadt
Hörtnag L, Wohlfahrt G (2014) Methane and nitrous oxide exchange over a managed hay meadow. Biogeosciences 11(24):7219–7236. https://doi.org/10.5194/bg-11-7219-2014
Küster FW, Thiel K, Fischbeck K (1962) Logarithmische rechentafel. Verlag Walter de Gruyter, Berlin, p 149
Lashermes G, Barriuso E, Le Villio-Poitrenaud M, Houot S (2012) Composting in small laboratory pilots: performance and reproducibility. Waste Manag 32:271–277. https://doi.org/10.1016/j.wasman.2011.09.011
Loyon L, Guiziou F, Béline F, Peu P (2007) Gaseous emissions (NH3, N2O, CH4 and CO2) from the aerobic treatment of piggery slurry—comparison with a conventional storage system. Biosyst Eng 97:472–480
Luo A, Zhu J, Ndegma PM (2001) Phosphorus transformations in swine manure during continous and intermittent aeration processes. Trans ASAE 44(4):967–972
Misselbrook T, Hunt J, Perazzolo F, Provolo G (2016) Greenhouse gas and ammonia emissions from slurry storage: impacts of temperature and potential mitigation through covering (pig slurry) or acidification (cattle slurry). J Environ Qual 45:1520–1530. https://doi.org/10.2134/jeq2015.12.0618
Moeletsi ME, Tongwane MI (2015) Methane and nitrous oxide emissions from manure management in South Africa. Animals 5(2):193–205. https://doi.org/10.3390/ani5020193
Monteny GJ, Bannink A, Chadwick D (2006) Greenhouse gas abatement strategies for animal husbandry. Agric Ecosyst Environ 112:163–170
Montes F, Meinen R, Dell C, Rotz A, Hristov AN, Oh J, Waghorn G, Gerber PJ, Henderson B, Makkar HPS, Dijkstra J (2013) Special topics—mitigation of methane and nitrous oxide emissions from animal operations: II A review of manure management mitigation options. J Anim Sci 91:5070–5094. https://doi.org/10.2527/jas2013-6584
Mostafa E, Buescher W (2011) Indoor air quality improvement from particle matters for laying hen poultry houses. Biosyst Eng 109:22–36
Mostafa E, Hoelscher R, Diekmann B, Ghaly AE, Buescher W (2017) Evaluation of two indoor air pollution abatement techniques in forced-ventilation fattening pig barns. Atmos Pollut Res 8:428–438
Ošlaj M, Muršec B (2010) Biogas as a renewable energy source. Tech Gaz 17(1):109–114
Park SH, Lee BR, Jung KH, Kim TH (2018) Acidification of pig slurry effects on ammonia and nitrous oxide emissions, nitrate leaching, and perennial ryegrass regrowth as estimated by 15N-urea flux. Asian-Aust J Anim Sci 31(3):457–466. https://doi.org/10.5713/ajas.17.0556
Pereira J, Trindade H (2014) Control of ammonia emissions in naturally ventilated dairy cattle facilities in Portugal. Engenharia Agrícola Journal 34(3):600–609. https://doi.org/10.1590/S0100-69162014000300022
Philippe F-X, Nicks B (2014) Review on greenhouse gas emissions from pig houses: production of carbon dioxide, methane and nitrous oxide by animals and manure. Agric Ecosyst Environ 199:10–25
Rojas-Downing MM, Nejadhashemi AP, Harrigan T, Woznicki SA (2017) Climate change and livestock: impacts, adaptation, and mitigation. Clim Risk Manag 16:145–163. https://doi.org/10.1016/j.crm.2017.02.001
Ruppert W, Stichlmair M, Bauchhenss J, Blendl HM, Haisch A, Hammer K, Hege U, Juli R, Melianl L, Nürnberger W, Rieder J, Rintelen P, Rutzmoser K, Weber W, Wurzinger A, Zeisig H (1985) Daten und Informationen zum Gülleeinsatz in der Landwirtschaft. Bayerisches Landwirtschaftliches Jahrbuch, Sonderheft, 62. Jahrgang 8:975–986
Sajeev EPM, Winiwarter W, Amon B (2018) Greenhouse gas and ammonia emissions from different stages of liquid manure management chains: abatement options and emission interactions. J Environ Qual 47:30–41. https://doi.org/10.2134/jeq2017.05.0199
Smith MPW, Evans MR (1982) The effects of low dissolved oxygen tension during the aerobic treatment of piggery slurry in complete mixed reactors. J Appl Microbiol 53:117–126
Sommer SG, Husted S (1995) The chemical buffer system in raw and digested animal slurry. J Agric Sci 124:45–53
Sommer SG, Clough TJ, Balaine N, Hafner SD, Cameron KC (2017) Transformation of organic matter and the emissions of methane and ammonia during storage of liquid manure as affected by acidification. J Environ Qual 46:514–521. https://doi.org/10.2134/jeq2016.10.0409
Thaer R (1978) Probleme der aeroben Behandlung von Flüssigmist in flüssiger Phase. Grundlagen Landtechnik 28:36–47
Wieland T, Sucrow W (1982) Die Praxis des organischen Chemikers, 43rd edn. Walter de Gruyter Verlag, Berlin, p 24
Acknowledgments
The authors acknowledge the financing organization USL (Umweltverträgliche und Standortgerechte Landwirtschaft). We would like also to thank the staff at the experimental station in Frankenforest and all colleagues at the Institute of Agricultural Engineering, Bonn University for providing the opportunity to conduct this research ‘or’ for helping us to complete this study successfully.
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Mostafa, E., Selders, A. & Buescher, W. Aeration of pig slurry affects ammonia and greenhouse gases emissions. Int. J. Environ. Sci. Technol. 16, 7327–7338 (2019). https://doi.org/10.1007/s13762-019-02388-2
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DOI: https://doi.org/10.1007/s13762-019-02388-2