NITROUS OXIDE EMISSIONS AND ITS INFLUENCING FACTORS INMAIZE FIELD

Authors

  • Yuzhou Jiang Institute of Agricultuwal Resources and Regional Planning, Chinese Academy of Agricultural Sciences, Beijing 100081, China , Key Laboratory of Eco-environment and Leaf Tobacco Quality, CNTC, Beijing 100081, China
  • Qingli Liu Institute of Agricultuwal Resources and Regional Planning, Chinese Academy of Agricultural Sciences, Beijing 100081, China , Key Laboratory of Eco-environment and Leaf Tobacco Quality, CNTC, Beijing 100081, China
  • Zhihong Li Institute of Agricultuwal Resources and Regional Planning, Chinese Academy of Agricultural Sciences, Beijing 100081, China , Key Laboratory of Eco-environment and Leaf Tobacco Quality, CNTC, Beijing 100081, China
  • Yungui Zhang Institute of Agricultuwal Resources and Regional Planning, Chinese Academy of Agricultural Sciences, Beijing 100081, China , Key Laboratory of Eco-environment and Leaf Tobacco Quality, CNTC, Beijing 100081, China
  • Yan Zou (Corresponding Author) Tobacco Science Institute of Guizhou Province, Guiyang 550000, China
  • Jingwei Zhu Tobacco Science Institute of Guizhou Province, Guiyang 550000, China
  • Junxiong Shi Tobacco Science Institute of Guizhou Province, Guiyang 550000, China
  • Heng Zhang Tobacco Science Institute of Guizhou Province, Guiyang 550000, China

Keywords:

N 2 O Emission, C/N Ratio, Yellow Cornfield, China, Environmental Factors.

Abstract

The experiment was conducted to explore the impact of different environmental factors on nitrous oxide (N 2 O) emission flux after application of fertilizer. An experiment was conducted in 2016 to determine the N 2 O emissions in maize yellow soil. There were three treatments: No fertilizer + Crop rotation for comparison (CK); inorganic fertilizer + Crop rotation (CR); inorganic fertilizer + Continuous cropping (CC). Therefore, the experiment was designed to study the variation features of N 2 O emissions in maize-growing season and analyze the impact of soil moisture, temperature and nitrate nitrogen content on N 2 O emissions after application of Crop rotation and Continuous cropping. The results indicated that: N 2 O emissions reached two peaks in maize-growing season, which mainly occurred in 1-11 days after application of Crop rotation and Continuous cropping; the cumulated amount of N 2 O emissions within 15 days after application of Crop rotation and Continuous cropping accounted for 22.16%-38.23% of the cumulated amount of N 2 O emissions during the whole growing season and total emission amount during growth period. Meanwhile, the average N 2 O emission flux of the three treatment process could be ranked as CC > CR > CK, which shall be measured as 0.056, 0.010 and 0.007 mg·m-2·h-1 respectively; The total N 2 O emissions of soil after application of Continuous cropping were improved for 7 times respectively as compared with single application of Crop rotation. According to relevant analysis, N 2 O emission flux of maize yellow soil was mainly related with the nitrate nitrogen content (P<0.05) in farmland, from which it could be concluded that N 2 O emission in maize yellow soil was free from any influence of local soil moisture content, air temperature or soil temperature. Moreover, N 2 O emissions of maize yellow soil were increased after application of Continuous cropping. Therefore, an important way to reduce N 2 O emissions of maize yellow soil was to control the application reasonable Crop rotation.

References

[1] Arvin Mosier, Carolien Kroeze, Cindy Nevison, et,all. Cleemput. Closing the global N 2 O budget: nitrous oxide emissions through the agricultural nitrogen cycle [J]. Nutrient Cycling in Agroecosystems, 1998, 52( 2/3):225-248.

[2] Li, C., Salas, Wand De Angelo, B., 2006. Assessing alternatives for mitigating net greenhouse gas emissions and increasing yields from rice production in China over the next twenty years. Journal of Environmental Quality., 35: 1554-1565.

[3] CAI Yan-jiang, DING Wei-xinand XIANG Jian, 2012. Mechanisms of Nitrous Oxide and Nitric Oxide Production in Soils: A Review. Soil., 05:712-718.

[4] ZHENG Xun-hua, WANG Ming-xingand WANG Yue-si, 1997. Impacts of Temperature on N 2 O Production and Emission. Environmental Science. 05:87-93.

[5] LIAO Qian-jiahuaand YAN Xiao-yuan, 2010. N 2 O Mitigation Effects and Economic Impacts from Enhanced-efficiency N Fertilizers from Fields in China. China Environmental Science., 12:1695-1701.

[6] Venterea R T, Halvorson A D, Kitchen N, LiebigMAand Cavigelli MA, 2012. Challenges and opportunities for mitigating nitrous oxide emissions from fertilized cropping systems. Frontiers in Ecology and the Environment, 10: 562-570.

[7] CHEN Zhe, CHEN Yuan-yuan, GAO Jiand LIU Ru-liang, 2015. Effects of Different Fertilization Measures on N 2 O Emission in Oil Sunflower Field in Irrigation Area of Upper Yellow River. Chinese Journal of Applied Ecology, 01:129-139.

[8] LI Yan-qing, TANG Ji-weiand CHE Sheng-guo, 2015. Effect of Organic and Inorganic Fertilizer on the Emission of CO2 and N 2 O from the Summer Maize Field in the North China Plain. Scientia Acricultura Sinica., 48: 4381-4389.

[9] ZENG Ze-bin, ZHU Boand ZHU Xue-mei, 2013. Effects of Fertilization on N 2 O Emission and Denitrification in Purple Soil during Summer Maize Season in the Sichuan Basin. Acta Pedologica Sinica., 50: 2013-130.

[10] HAO Xiao-yu, ZHOU Bao-kuand MA Xing-zhu, 2015. Effects of Nitrogen Fertilizer Management on Greenhouse Gas Emissions from Maize Field in Black Soil. China Environmental Science., 35: 3227-3238.

[11] GAO Lin, 2016. Researches on Greenhouse Gases Emission under Different Farming from Dryland Farming. Anhui Agriculture University.

[12] HOU Hui-jing, CHEN Huiand YANG Shi-hong, 2015. Effects of Controlled Irrigation of Paddy Fields on N 2 O Emissions from Rice-Winter Wheat Rotation Systems. Transactions of the Chinese Society of Agricultural Engineering. 12:5-131.

[13] Bao Shi-dan.2000. Soil Agro-chemistrical Analysis. China Agriculture Press.

[14] Diao Tian-tian, Xie Li-yongand Guo Li-ping, 2013. Measurements of N 2 O emissions from different vegetable fields on the North China Plain. Atmospheric Environment, 72: 70-76.

[15] WANG Li-gang, LI Hu, QIU Jian-jun, 2008.Characterization of emissions of nitrous oxide from soils of typical crop field in Huang-Huai-Hai Plain. Scientia Agricultura Sinica, 41 ( 4 ): 1248-1254.

[16] Bouwman AF, 1996. Direct emission of nitrous oxide from agricultural soils. Nutrient Cycling in Agroecosystems,46: 53-70.

[17] Liu Xing, Zhang Shule, Liu Guofeng, 2014. Effects of Continuous cropping on dry matter accumulation and distribution of potato plants in the yellow river irrigation areas of Middle Gansu Province. Acta Agronomica Sinica, 40(07):1274-1285.

[18] Zou G Y, Zhang F S, Xiao tang J U, Chen XP andLiuXJ, 2004. Study on soil denitrification in winter wheat-summer maize rotation system. Scientia Agricultura Sinica., 37: 1492-1496.

[19] SHAN Nan, ZHAO Tong-keand BI Xiao-qing, 2016. Suitable Nitrogen Application Reducing N 2 O Emission and Improving Grain Yield in Wheat-maize Crop Rotation System in Beijing Suburb. Transactions of the Chinese Society of Agricultural Engineering, 22:163-170.

[20] Hu Teng, Tong Yanan, Gao Pengcheng, 2014. N 2 O emission characteristics and mitigation methods in South Loess Plateau under rain-f

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Published

2019-10-30

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How to Cite

Jiang Yuzhou, Liu Qingli, Li Zhihong, Zhang Yungui, Zou Yan , Zhu Jingwei, Shi Junxiong, Zhang Heng. Nitrous oxide emissions and its influencing factors inmaize field. Eurasia Journal of Science and Technology. 2019, 1(1): 26-31.