Methane, nitrous oxide and ammonia generation in full-scale swine wastewater purification facilities

  • Takashi Osada
  • Makoto Shiraishi
  • Teruaki Hasegawa
  • Hirofumi Kawahara
Research Article
Part of the following topical collections:
  1. Livestock Waste Management and Resource Recovery

Abstract

The activated sludge process to remove nitrogen and biochemical oxygen demand (BOD) is reportedly cost-effective for swine wastewater treatment, and it use has thus increased in pig farming. Nitrous oxide (N2O) is generated on farms as an intermediate product in nitrification and denitrification, and methane (CH4) is also generated from organic degradation under anaerobic conditions by microorganisms in manure or wastewater. This study was carried out at five activated sludge treatment facilities across Japan between August 2014 and January 2015. Measurements were conducted over several weeks at wastewater purification facilities for swine farms: two in Chiba prefecture (East Japan), two in Okayama prefecture (West Japan), and one in Saga (Southern Japan). Taking several environmental fluctuations into account, we collected measurement data continuously day and night, during both high-temperature and low-temperature periods. The results indicated that CH4 and N2O emission factors were 0.91% (kgCH4∙kg volatile solids–1) and 2.87% (g N2O-N∙kg total N–1), respectively. Ammonia emissions were negligible in all of the measurements from the wastewater facilities. The N2O emission factor calculated under this experiment was low compared to our previous finding (5.0%; g N2O-N∙kg N–1) in a laboratory experiment. In contrast, the CH4 emission factor calculated herein was rather high compared to the laboratory measurements. There was great variation in daily GHG emission factors measured in the actual wastewater treatment facilities. In particular, the N2O emission rate was affected by several environmental conditions at each facility location, as well as by the management of the wastewater treatment.

Keywords

Manure Greenhouse gas Denitrification BOD/N Nitrous oxide Methane 

Notes

Acknowledgements

We express our appreciation for the financial support from the Minister’s Secretariat, Ministry of Agriculture, Forestry and Fisheries Japan. This study was supported by Japanese Ministry of Agriculture, Forestry and Fisheries, via the Commissioned project study.

References

  1. 1.
    Tsuiki M. and Harada Y. A computer program for estimating the amount of livestock wastes. The Journal of the Japanese Agricultural Systems Society, 1997, 13(1): 17–23Google Scholar
  2. 2.
    Haga K. Animal waste problems and their solution from the technological point of view in Japan. Jpn Agric Res Q, 1998, 32(3): 203–210Google Scholar
  3. 3.
    Tilman D, Cassman K G, Matson P A, Naylor R, Polasky S. Agricultural sustainability and intensive production practices. Nature, 2002, 418(6898): 671–677CrossRefGoogle Scholar
  4. 4.
    Kampschreur M J, Temmink H, Kleerebezem R, Jetten M S M, van Loosdrecht M C M. Nitrous oxide emission during wastewater treatment. Water Research, 2009, 43(17): 4093–4103CrossRefGoogle Scholar
  5. 5.
    Greenhouse Gas Inventory Office of Japan, National Greenhouse Gas Inventory Report of Japan. Ministry of the Environment, Japan, 2015URL: http://www-gio.nies.go.jp/.Google Scholar
  6. 6.
    Intergovernmental Panel on Climate Change. Climate Change 2007: The Physical Science Basis. 2007 (Intergovernmental Panel on Climate Change: Stockholm). URL: https://www.ipcc.ch/publications_and_data/publications_ipcc_fourth_assessment_report_wg1_ report_the_physical_science_basis.htm. (Accessed March 7, 2017)Google Scholar
  7. 7.
    Crutzen P J. Atmospheric chemical processes of the oxides of nitrogen, including nitrous oxide. In: Delwiche C C, ed. Denitrification, Nitrification and Atmospheric Nitrous Oxide. New York: John Wiley and Sons,1981, 17–44Google Scholar
  8. 8.
    Osada T, Kuroda K, Yonaga M. Reducing nitrous oxide gas emissions from fill-and-draw type activated sludge process. Water Research, 1995, 29(6): 1607–1608CrossRefGoogle Scholar
  9. 9.
    Kampschreura M J, Temmink H, Kleerebezema R, Jettena M S M, van Loosdrecht M C M. Nitrous oxide emission during wastewater treatment. Water Research, 2009, 43(17): 4093–4103CrossRefGoogle Scholar
  10. 10.
    Osada T. Nitrous oxide emission from purification of liquid portion of swine wastewater. In: Greenhouse Gas Control Technologies, Sixth International Conference. Gale J, Kaya Y, eds. Oxford,2003, 1299–1304CrossRefGoogle Scholar
  11. 11.
    Sherman M H. Tracer-gas techniques for measuring ventilation in a single zone. Building and Environment, 1990, 25(4): 365–374CrossRefGoogle Scholar
  12. 12.
    American Public Health Association (APHA), American Water Works Association (AWWA), and Water Environment Federation (WEF). Standard Methods for the Examination of Water and Wastewater, 22nd edition. Rice EW, Baird R B, Eaton A D, Clesceri L S, eds. Washington D C: American Public Health Association, 2012Google Scholar
  13. 13.
    Minato K, Kouda Y, Yamakawa M, Hara S, Tamura T, Osada T. Determination of GHG and ammonia emissions from stored dairy cattle slurry by using a floating dynamic chamber. Animal Science Journal, 2013, 84(2): 165–177CrossRefGoogle Scholar
  14. 14.
    Vanderzaag A C, Flesch T K, Desjardins R L, Balde H, Wright T. Measuring methane emissions from two dairy farms: seasonal and manure-management effects. Agricultural Meteorology, 2014, 194: 259–267CrossRefGoogle Scholar
  15. 15.
    Intergovernmental Panel on Climate Change (IPCC). The Revised Guidelines for National Greenhouse Gas Inventories. Reference manual, Vol. III. United Nations, New York, 1996, URL: http:// www.ipcc-nggip.iges.or.jp/public/gl/invs6.html. (Accessed March 6, 2017)Google Scholar
  16. 16.
    IPCC (Intergovernmental Panel on Climate Change). 2006 IPCC Guidelines for National Greenhouse Gas Inventories, Prepared by the National Greenhouse Gas Inventories Programme. Eggleston H S, Buendia L, Miwa K, Ngara T, Tanabe K, eds. Published: IGES, Japan. Chapter 10: Emissions from Livestock and Manure Management. In: Volume 4 Agriculture, Forestry and Other Land Use, 2006, URL: http://www.ipcc-nggip.iges.or.jp/public/2006gl/. (Accessed March 6, 2017)Google Scholar
  17. 17.
    Osada T, Kuroda K, Yonaga M. Reducing nitrous oxide gas emissions from fill-and-draw type activated sludge process. Water Research, 1995, 29(6): 1607–1608CrossRefGoogle Scholar
  18. 18.
    Yamashita T, Shiraishi M, Yamamoto-Ikemoto R, Yokoyama H, Ogino A, Osada T. Swine wastewater treatment technology to reduce nitrous oxide emission by using an aerobic bioreactor packed with carbon fibres. Animal Production Science, 2016, 56(3): 330–336CrossRefGoogle Scholar
  19. 19.
    Guisasola A, de Haas D, Keller J, Yuan Z. Methane formation in sewer systems. Water Research, 2008, 42(6-7): 1421–1430CrossRefGoogle Scholar
  20. 20.
    Hwang K L, Bang C H, Zoh K D. Characteristics of methane and nitrous oxide emissions from the wastewater treatment plant. Bioresource Technology, 2016, 214: 881–884CrossRefGoogle Scholar
  21. 21.
    Vanderzaag A C, Gordon R J, Burton D L, Jamieson R C, Stratton G W. Greenhouse gas emissions from surface flow and subsurface flow constructed wetlands treating dairy wastewater. Journal of Environmental Quality, 2010, 39(2): 460–471CrossRefGoogle Scholar
  22. 22.
    Wang J, Zhang J, Xie H, Qi P, Ren Y, Hu Z. Methane emissions from a full-scale A/A/O wastewater treatment plant. Bioresource Technology, 2011, 102(9): 5479–5485CrossRefGoogle Scholar
  23. 23.
    Ogink N W M, Mosquera J, Calvet S, Zhang G. Methods for measuring gas emissions from naturally ventilated livestock buildings: developments over the last decade and perspectives for improvement. Biosystems Engineering, 2013, 116(3): 297–308CrossRefGoogle Scholar
  24. 24.
    Hu Z, Zhang J, Xie H, Li S, Wang J, Zhang T. Effect of anoxic/ aerobic phase fraction on N2O emission in a sequencing batch reactor under low temperature. Bioresource Technology, 2011, 102 (9): 5486–5491CrossRefGoogle Scholar
  25. 25.
    Paudel S R, Choi O, Khanal S K, Chandran K, Kim S, Lee J W. Effects of temperature on nitrous oxide (N2O) emission from intensive aquaculture system. Science of the Total Environment, 2015, 518: 16–23CrossRefGoogle Scholar
  26. 26.
    Holtan-Hartwig L, Dösch P, Bakken L R. Low temperature control of soil denitrifying communities: kinetics of N2O production and reduction. Soil Biology and Biochemistry, 2002, 34(11): 1797–1806CrossRefGoogle Scholar
  27. 27.
    Hanaki K, Hong Z, Matsuo T. Production of nitrous oxide gas during denitrification of wastewater. Water Science and Technology, 1992, 26: 1027–1036Google Scholar
  28. 28.
    DaelmanMR J, van Voorthuizen EM, van Dongen U G JM, Volcke E I P, van Loosdrecht M C M. Seasonal and diurnal variability of N2O emissions from a full-scale municipal wastewater treatment plant. Science of the Total Environment, 2015, 536: 1–11CrossRefGoogle Scholar

Copyright information

© Higher Education Press and Springer-Verlag Berlin Heidelberg 2017

Authors and Affiliations

  • Takashi Osada
    • 1
  • Makoto Shiraishi
    • 2
  • Teruaki Hasegawa
    • 3
  • Hirofumi Kawahara
    • 4
  1. 1.National Agriculture and Food Research OrganizationTsukuba, IbarakiJapan
  2. 2.Okayama Prefectural Center for Animal Husbandry ResearchMisaki, OkayamaJapan
  3. 3.Chiba Prefectural Livestock Research CenterYachimata, ChibaJapan
  4. 4.Saga Prefectural Higashimastuura Agricultural Development and Extension CenterKaratsu, SagaJapan

Personalised recommendations