Journal of The Korean Society of Grassland and Forage Science (한국초지조사료학회지)

The Korean Society of Grassland and Forage Science (한국초지조사료학회)
권호 표지
DOI QR코드

DOI QR Code

Ammonification and NH3 emission in the Soil Amended with Different Animal Manures

  • Wang, Xin-Lei (Department of Animal Science, Institute of Agriculture Science and Technology, College of Agriculture & Life Science) ;
  • Zhang, Qian (Department of Animal Science, Institute of Agriculture Science and Technology, College of Agriculture & Life Science) ;
  • Park, Sang-Hyun (Department of Animal Science, Institute of Agriculture Science and Technology, College of Agriculture & Life Science) ;
  • Lee, Bok-Rye (Department of Animal Science, Institute of Agriculture Science and Technology, College of Agriculture & Life Science) ;
  • Kim, Tae-Hwan (Department of Animal Science, Institute of Agriculture Science and Technology, College of Agriculture & Life Science)
  • Received : 2017.01.31
  • Accepted : 2017.03.21
  • Published : 2017.03.30
Download PDF
⟨ Previous Next ⟩

Abstract

Mineralization is an important biological process for conversion of organic nitrogen (N) to inorganic N which can be used by plants directly. To investigate the effect of different manures on soil mineralization, the soil amended with cattle (CtM), goat (GM), chicken manure (ChM) and pig slurry (PS) were incubated under in vitro condition and ammonium N ($NH_4{^+}-N$), ammonification rate and ammonia emission were determined for eighty-four days. $NH_4{^+}-N$ was the highest in PS-amended soil for the whole experimental period. $NH_4{^+}-N$ in PS-amended soil was gradually decreased until day 84, whereas it was rapidly decreased for the first 14 days and then slightly increased until 84 days in ChM-, CtM- and GM-amended soil. The ammonification rate showed negative value for the first 14 days in all treatments. From day 14, ammonification rate started to increase in CtM- and ChM-amended soil, whereas it was maintained in GM- and PS-amended soil until day 84. The daily ammonia emission was the highest in PS-amended soil ($41mg\;kg^{-1}d^{-1}$), followed by CtM-, ChM-, and GM-amended soil at day 1. It was gradually decreased until day 84 in all treatments. The total $NH_3$ emission was the highest in PS-amended soil with $0.6mg\;kg^{-1}$ for 84 days, while less than $0.1mg\;kg^{-1}$ in three other plots. These results indicate that different manures showed different soil ammonification rate and $NH_3$ emission.

Keywords

References

  1. Badia, D. 2000. Potential nitrification rates of semiarid cropland soils from the Central Ebro Valley, Spain. Arid Soil Research and Rehabilitation. 14:281-292. https://doi.org/10.1080/089030600406680
  2. Bremner, J.M. 1996. Nitrogen-total. In: Sparks, D.L., Page, A.L., Helmke, P.A., Loeppert, R.H., Soltanpour, P.N., Tabatabai, M.A., Johnston, C.T. and Sumner, M.E. (Eds) Methods of soil analysis. Part 3: chemical methods. SSSA Book Series 5. SSSA and ASA. Madison. pp .1085-1121.
  3. Cassman, K.G. and Munns, D.N. 1980. Nitrogen mineralization as affected by soil moisture, temperature, and depth. Soil Science Society of America Journal 44: 1233-1237. https://doi.org/10.2136/sssaj1980.03615995004400060020x
  4. Chambers, B.J., Smith, K. and van der Weerden, T.J. 1997. Ammonia emissions following the land spreading of solid manures. In: Jarvis, S.C., Pain, B.F. (Eds.), Gaseous nitrogen emissions from grasslands. CAB International Wallingford, pp. 275-280.
  5. Eckard, R.J., Chen, D., White, R.E. and Chapman, D.F. 2003. Gaseous nitrogen loss from temperate perennial grass and clover dairy pastures in south-eastern Australia. Australian Journal of Agricultural Research. 54(6): 561-570. https://doi.org/10.1071/AR02100
  6. Eghball, B. 2000. Nitrogen mineralization from field-applied beef cattle feedlot manure or compost. Soil Science Society of America Journal 64: 2024-2030. https://doi.org/10.2136/sssaj2000.6462024x
  7. Eghball, B., Wienhold, B.J., Gilley, J.E. and Eigenberg, R.A. 2002. Mineralization of manure nutrients. Journal of Soil and Water Conservation 57: 470-473.
  8. Harris, R.F. 1981. Effect of water potential on microbial growth and activity. Water Potential Relations in Soil Microbiology. Soil Science Society America, Madison, WI, pp. 23-95.
  9. Haynes, R.J. 1986. Mineral nitrogen in the plant-soil system. Academic Press, Orlando, Florida. pp. 127-165.
  10. Hristov, A.N., Hanigan, M., Cole, A., Todd, R., McAllister, T.A., Ndegwa, P.M. and Rotz, A. 2011. Ammonia emissions from dairy farms and beef feedlots: A review. Canadian Journal of Animal Science. 91:1-35. https://doi.org/10.4141/CJAS10034
  11. Khalil, M. I., Hossain, M. B. and Schmidhalter, U. 2005. Carbon and nitrogen mineralization in different upland soils of the subtropics treated with organic materials. Soil Biology and Biochemistry. 37: 1507-1518. https://doi.org/10.1016/j.soilbio.2005.01.014
  12. Kim, T.H. and Kim, B.H. 1996. Ammonia microdiffusion and colorimetric method for determining nitrogen in plant tissues. Journal of the Korean Society of Grassland Science. 16:253-259.
  13. Kirkham, D. and Bartholomew, W.V. 1954. Equations for following nutrient transformations in soil utilizing tracer data. Soil Science II Society Proceedings. 19:189-192.
  14. Krogdahl, A. and Dalsgard, B. 1981. Estimation of nitrogen digestibility in Poultry. Content and distribution of major urinary nitrogen compounds in excreta. Poultry Science.60:2480-2485. https://doi.org/10.3382/ps.0602480
  15. Li, L.L. and Li, S.T. 2014. Nitrogen mineralization from animal manures and its relation to organic N fractions. Journal of Integrative Agriculture. 13(9): 2040-2048. https://doi.org/10.1016/S2095-3119(14)60769-3
  16. Lu, R. 2000. Soil Agricultural Chemical Analysis Methods. China Agricultural Science and Technology Press, Beijing.
  17. Matsusada J., Maeda, T. and Ohmiya, K. 2002. Ammonia emissions from composting of livestock manure. In: Takahashi, J. and Young, B.A. (Ed). Proceedings of the 1st International Conference on Greenhouse Gases and Animal Agriculture, Elsevier Science Inc., Amsterdam, pp. 283-286.
  18. Moller, K. and Stinner, W. 2009. Effects of different manuring systems with and without biogas digestion on soil mineral nitrogen content and on gaseous nitrogen losses (ammonia, nitrous oxides). European Journal of Agronomy. 30:1-16. https://doi.org/10.1016/j.eja.2008.06.003
  19. Pagans, E., Barrena R., Font X. and Sanchez, A. 2006. Ammonia emissions from the composting of different organic wastes: dependency on process temperature. Chemosphere. 62: 1534-1542. https://doi.org/10.1016/j.chemosphere.2005.06.044
  20. Park, S.H., Lee, B.R. and Kim, T.H. 2015. Effects of cattle manure and swine slurry acidification on ammonia emission as estimated by an acid trap system. Journal of the Korean Society of Grassland Science. 35: 212-216. https://doi.org/10.5333/KGFS.2015.35.3.212
  21. Park, S.H., Lee, B.R. and Kim, T.H. 2016. Effect of dicyandiamide and hydroquinone on ammonia and nitrous oxide emission from pig slurry applied to Timothy (Phleum pretense L.) sward. Journal of the Korean Society of Grassland Science. 36: 199-204. https://doi.org/10.5333/KGFS.2016.36.3.199
  22. Roy, R.N., Misira, R.V. and Montanez, A. 2002. Decreasing reliance on mineral nitrogen-yet more food. Ambio. 31:177-183. https://doi.org/10.1579/0044-7447-31.2.177
  23. Salazar, F., Martinez-Lagos, J., Alfaro, M. and Misselbrook, T. 2014. Ammonia emission from a permanent grassland on volcanic soil after the treatment with dairy slurry and urea. Atmospheric Environment. 95: 591-597. https://doi.org/10.1016/j.atmosenv.2014.06.057
  24. Sanderson, M.G., Collins, W.J., Johnson, C.E. and Derwent, R.G. 2006. Present and future acid deposition to ecosystems: The effect of climate change. Atmospheric Environment. 40: 1275-1283. https://doi.org/10.1016/j.atmosenv.2005.10.031
  25. Wolter, M., Prayitno, S. and Schuchardt, F. 2004. Greenhouse gas emission during storage of pig manure on a pilot scale. Bioresource Technology. 95: 235-244. https://doi.org/10.1016/j.biortech.2003.01.003