DOI QR코드

DOI QR Code

신개발 심층시비장치를 이용한 심층시비의 밭작물 재배 효과

Understanding the Effects of Deep Fertilization on Upland Crop Cultivation and Ammonia Emissions using a Newly Developed Deep Fertilization Device

  • 홍성창 (농촌진흥청 국립농업과학원 기후변화평가과) ;
  • 김민욱 (농촌진흥청 국립농업과학원 기후변화평가과) ;
  • 김진호 (농촌진흥청 국립농업과학원 기후변화평가과) ;
  • 박성직 (국립한경대학교 지역자원시스템공학부)
  • Sung-Chang Hong (Climate Change & Assessment Division, National Institute of Agricultural Sciences, Rural Development Administration) ;
  • Min-Wook Kim (Climate Change & Assessment Division, National Institute of Agricultural Sciences, Rural Development Administration) ;
  • Jin-Ho Kim (Climate Change & Assessment Division, National Institute of Agricultural Sciences, Rural Development Administration) ;
  • Seong-Jik Park (Department of Bioresources and Rural System Engineering, Hankyoung National University)
  • 투고 : 2023.03.17
  • 심사 : 2023.03.24
  • 발행 : 2023.03.31

초록

Nitrogen fertilizers applied to agricultural lands for crop cultivation can be volatilized as ammonia. The released ammonia can catalyze the formation of ultrafine dust (particulate matter, PM2.5), classified as a short-lived climate change pollutant, in the atmosphere. Currently, one of the prominent methods for fertilizer application in agricultural lands is soil surface application, which comprises spraying the fertilizers onto the soil surface, followed by mixing the fertilizers with the soil. Owing to the low nitrogen absorption rate of crops, when nitrogen fertilizers are applied in this manner, they can be lost from land surfaces through volatilization. Therefore, investigating a new fertilization method to reduce ammonia emissions and increase the fertilizer utilization efficiency of crops is necessary. In this study, to develop a method for reducing ammonia emissions from nitrogen fertilizers applied to soil surfaces, deep fertilization was conducted using a newly developed deep fertilization device, and ammonia emissions from barley, garlic, and onion fields were examined. Conventional fertilization (surface application) and deep fertilization (soil depth of 25 cm) were conducted for analysis. The fertilization rate was 100% of the standard fertilization rate used for barley, and deep fertilization of N, P, and K fertilizers was implemented. Ammonia emissions were collected using a wind tunnel chamber, and quantified subsequently susing the indole-phenol blue method. Ammonia emissions released from the basal fertilizer application persisted for approximately 58 d, beginning from approximately 3 d after fertilization in conventional treatments; however, ammonia was not released from deep fertilization. Moreover, barley, garlic, and onion yields were higher in the deep fertilization treatment than in the conventional fertilization treatment. In conclusion, a new fertilization method was identified as an alternative to the current approach of spraying fertilizers on the soil surface. This new method, which involves injecting nitrogen fertilizers at a soil depth of 25 cm, has the potential to reduce ammonia emissions and increase the yields of barley, garlic, and onion.

키워드

과제정보

This study was carried out with the support of "Research Program for Agricultural Science & Technology Development (Project No. PJ016998)", National Institute of Agricultural Sciences, Rural Development Administration, Republic of Korea.

참고문헌

  1. Liu TQ, Fan DJ, Zhang XX, Chen J, Li CF, Cao CG (2015) Deep placement of nitrogen fertilizers reduces ammonia volatilization and increases nitrogen utilization efficiency in no-tillage paddy fields in central China. Field Crops Research, 184, 80-90. https://doi.org/10.1016/j.fcr.2015.09.011.
  2. Wu P, Liu F, Li H, Cai T, Zhang P, Jia Z (2021) Suitable fertilizer application depth can increase nitrogen use efficiency and maize yield by reducing gaseous nitrogen losses. Science of the Total Environment, 781, 146787. https://doi.org/10.1016/j.scitotenv.2021.146787.
  3. Du B, Luo HW, He LX, Zheng AX, Chen YL, Zhang TT, Wang ZM, Hu L, Tang XR (2018) Deep fertilizer placement improves rice growth and yield in zero tillage. Applied Ecology and Environmental Research, 16(6), 8045-8054. http://dx.doi.org/10.15666/aeer/1606_80458054.
  4. Chatterjee D, Mohanty S, Guru PK, Swain CK, Tripathi R, Shahid M, Kumar U, Kumar A, Bhattacharyya P et al. (2018) Comparative assessment of urea briquette applicators on greenhouse gas emission, nitrogen loss and soil enzymatic activities in tropical lowland rice. Agriculture, Ecosystems and Environment, 252, 178-190. https://doi.org/10.1016/j.agee.2017.10.013.
  5. Kim TY, Kim SY, Hong H C, Hong BY, Lee YB (2013) Evaluation of ammonia emission from liquid pig manure composting system with forced aeration. Korean Journal of Environmental Agriculture, 32(4), 366-368. https://doi.org/10.5338/KJEA.2013.32.4.366.
  6. Liu TQ, Li SH, Guo LG, Cao CG, Li CF, Zhai ZB, Zhou JY, Mei YM, Ke HJ (2020) Advantages of nitrogen fertilizer deep placement in greenhouse gas emissions and net ecosystem economic benefits from no-tillage paddy fields. Journal of Cleaner Production, 263, 121322. https://doi.org/10.1016/j.jclepro.2020.121322.
  7. Wu P, Chen G, Liu F, Cai T, Zhang P, Jia Z (2021) How does deep-band fertilizer placement reduce N2O emissions and increase maize yields?. Agriculture, Ecosystems and Environment, 322, 107672. https://doi.org/10.1016/j.agee.2021.107672.
  8. Liu W, Xiong Y, Xu X, Xu F, Hussain S, Xiong H, Yuan J (2019) Deep placement of controlled release urea effectively enhanced nitrogen use efficiency and fresh ear yield of sweet corn in fluvoaquic soil. Scientific Reports, 9(1), 1-11. https://doi.org/10.1038/s41598-019-56912-y.
  9. Linquist BA, Adviento-Borbe MA, Pittelkow CM, van Kessel C, van Groenigen KJ (2012) Fertilizer management practices and greenhouse gas emissions from rice systems: A quantitative review and analysis. Field Crops Research, 135, 10-21. https://doi.org/10.1016/j.fcr.2012.06.007.
  10. Fan J, McConkey B, Wang H, Janzen H (2016) Root distribution by depth for temperate agricultural crops. Field Crops Research, 189, 68-74. https://doi.org/10.1016/j.fcr.2016.02.013.