DOI QR코드

DOI QR Code

Estimation of Ammonia Emission with Compost Application in Plastic House for Leafy Perilla Cultivation

시설잎들깨 재배의 퇴비 시용에 의한 암모니아 배출량

  • Hong, Sung-Chang (Climate Change & Evaluation Division, Department of Agricultural Environment, National Institute of Agricultural Sciences, Rural Development Administration) ;
  • Kim, Jin-Ho (Climate Change & Evaluation Division, Department of Agricultural Environment, National Institute of Agricultural Sciences, Rural Development Administration) ;
  • Kim, Min-Wook (Climate Change & Evaluation Division, Department of Agricultural Environment, National Institute of Agricultural Sciences, Rural Development Administration)
  • 홍성창 (농촌진흥청 국립농업과학원 농업환경부 기후변화평가과) ;
  • 김진호 (농촌진흥청 국립농업과학원 농업환경부 기후변화평가과) ;
  • 김민욱 (농촌진흥청 국립농업과학원 농업환경부 기후변화평가과)
  • Received : 2021.05.19
  • Accepted : 2021.08.24
  • Published : 2021.09.30

Abstract

BACKGROUND: Concerns have been raised about the impact of recent high concentrations of fine dust on human health. Ammonia(NH3) reacts with sulfur oxides and nitrogen compounds in the atmosphere to form ultrafine ammonium sulfate and ammonium nitrate (PM2.5). There is a growing need for accurate estimates of the amount of ammonia emitted during agricultural production. Therefore, in this study, ammonia emissions generated from the cultivation of leafy perilla in plastic houses were determined. METHODS AND RESULTS: Cow manure compost, swine manure compost, and poultry manure compost each at 34.6 ton ha-1, the amount commonly used by farmers in the field, was sprayed on the soil surface. Just after spraying cow manure compost, swine manure compost, and poultry manure compost, the ammonia was periodically measured and analyzed to be 22.5 kg ha-1, 22.8 kg ha-1, and 85.2 kg ha-1, respectively. The emission factors were estimated at 70.0 kg-NH3 ton-N, 62.8 kg-NH3 ton-N, and 234.1 kg-NH3 ton-N, respectively. Most ammonia was released in the two weeks after application of the compost and then the amount released gradually decreased. CONCLUSION: Therefore, it is necessary to improve the emission factor through a study on the estimation of ammonia emission by type of livestock manure and major farming types such as rice fields and uplands, and to update data on the production, distribution, and sales of livestock manure.

Keywords

Acknowledgement

This study was carried out with the support of "Research Program for Agricultural Science & Technology Development (Project No. PJ014206)", National Institute of Agricultural Sciences, Rural Development Administration, Republic of Korea.

References

  1. Hristov AN (2011) Contribution of ammonia emitted from livestock to atmospheric fine particulate matter (PM2.5) in the United States. Journal of American Dairy Science, 94(6), 3130-3136. https://doi.org/10.3168/jds.2010-3681.
  2. Domingo NGG, Balasubramanian S, Thakrar SK, Clark MA, Adams PJ, Marshall JD, Muller NZ, Pandis SN, Polasky S et al. (2021) Air quality-related health damages of food. Proceedings of the National Academy of Sciences, 118(20), e2013637118. https://doi.org/10.1073/pnas.2013637118.
  3. Jiang B, Xia D (2017) Role identification of NH3 in atmospheric secondary new particle formation in haze occurrence of China. Atmospheric Environment, 163, 107-117. https://doi.org/10.1016/j.atmosenv.2017.05.035.
  4. Wu Y, Gu BJ, Erisman JW, Reis S, Fang YY, Lu XH, Zhang XM (2016) PM 2.5 pollution is substantially affected by ammonia emissions in China. Environmental Pollution, 218, 86-94. https://doi.org/10.1016/j.envpol.2016.08.027.
  5. Suanne W, Elisabeth A, Olga B, Jurgen Z (2015) Costs and benefits of ammonia and particulate matter abatement in German agriculture including interactions with greenhouse gas emissions. Agriculural Systems, 141, 58-68. https://doi.org/10.1016/j.agsy.2015.09.003.
  6. Kim ST, Bae CH, Kim BU, Kim HC (2017) PM 2.5 simulations for the Seoul metropolitan area: (I) Contributions of precursor emissions in the 2013 CAPSS emissions inventory. Journal of Korean Society for Atmospheric Environment, 33(2), 139-158. https://doi.org/10.5572/KOSAE.2017.33.2.139.
  7. Gong L, Lewicki R, Griffin RJ, Tittel FK, Lonsdale CR, Srevens RG, Pierce JR (2013) Role of atmospheric ammonia in particulate matter formation in Houston during summertime. Atmospheric Environment, 77, 893-900. https://doi.org/10.1016/j.atmosenv.2013.04.079.
  8. Zhao ZQ, Bai ZH, Winiwarter W, Kiesewetter G, Heyes C, Ma L (2017) Mitigating ammonia emission from agriculture reduces PM2.5 pollution in the Hai River Basin in China. Science of The Total Environment, 609, 1152-1160. https://doi.org/10.1016/j.scitotenv.2017.07.240.
  9. WU SP, Zhnag YJ, Scwab JJ, Li YF, Liu YL, Yuan CS (2017) High-resolution ammonia emissions inventories in Fujian, China, 2009-2015. Atmospheric Environment, 162, 100-114. https://doi.org/10.1016/j.atmosenv.2017.04.027.
  10. Reis S, Howard C, Sutton MA (2015) Cost of ammonia abatement and the climate co-benefits, p. 4, London Springer, UK.
  11. Shin DW, Joo HS, Seo EJ, Kim CY (2017) Management strategies to reduce PM 2.5 emission: emphasisammonia, pp. 69-70, Korea Environment Institute, Korea.
  12. Yun HB, Lee Y, Lee SM, Kim SC, Lee YB (2008) Evlauation of ammonia emission following application techniques of pig manure compost in upland soil. Korean Journal of Environmental Agriculture, 28(1), 15-19. https://doi.org/10.5338/KJEA.2009.28.1.015.
  13. Meisinger, J.J., Lefcourt, A. M., Thompson, R. B. (2001) Construction and validation of small mobile wind tunnels for studying ammonia volatilization. Applied Engineering of Agriculture, 17, 375-381.
  14. Missellbrook TH, Smith KA, Johnson RA, Pain BF (2002) Slurry application techniques to reduce ammonia emissions: results of some UK field-scale experiments. Biosystems Engineering, 81(3), 313-321. https://doi.org/10.1006/bioe.2001.0017.
  15. Atia A (2008) Ammonia volatilization from manure application. https://open.alberta.ca/dataset/4182162/resource/863253f1-22f1-4a7b-950a-c424ef5cc9e5.
  16. Ku HH (2020) Measurement of soil surface and plant canopy ammonia flexes in red pepper fields using dynamic chamber method. Korean Journal of Soil Science and Fertilizer, 53(4), 643-649. https://doi.org/10.7745/KJSSF.2020.53.4.643.
  17. Hayashi K, Nishimura S, Yagi K (2008) Ammonia volatilization from a paddy field following applications of urea: rice plants are both an absorber and an emitter for atmospheric ammonia. Science of the Total Environment, 390(2-3), 485-494. https://doi.org/10.1016/j.scitotenv.2007.10.037.
  18. Le PD, Aarnink AJA, Ogink NWM, Becker PM, Verstegen MWA (2005) Odor from animal production facilities: its relationship to diet. Nutrition Research Reviews, 18, 3-30. https://doi.org/10.1079/NRR200592.
  19. De-Xi L, Xiao-Hui F, Feng H, Hong-Tao Z, Jia-Fa L (2007) Ammonia volatilization and nitrogen utilization efficiency in response to urea application in rice fields of the Taihu Lake region, China. Pedosphere, 17(5), 639-645. https://doi.org/10.1016/S1002-0160(07)60076-9.
  20. Wang HG, Zhang D, Zhang Y, Zhai L, Yin B, Zhou B, Geng Y, Pan J, Luo BJ et al. (2018) Ammonia emissions from paddy fields are underestimated in China. Environmental Pollution, 235, 482-488. https://doi.org/10.1016/j.envpol.2017.12.103.
  21. Park SM, Kim SN, Hong CH (2020) Effect of reducing ammonia volitilization from the arable soil with iron sulfate. Korean Journal of Soil Science and Fertilizer, 53(4), 405-414. https://doi.org/10.7745/KJSSF.2020.53.4.405.
  22. Lee SM, L JH, Park JH, Hwang SW, Seo DC (2020) Characteristics of ammonia gas emission from soybean cultivation soil with biochar, fly ash, and microorganisms. Korean Journal of Soil Science and Fertilizer, 53(4), 528-537. https://doi.org/10.7745/KJSSF.2020.53.4.528.