Effect of biofertilizer and wheat straw biochar application on nitrous oxide emission and ammonia volatilization from paddy soil

被引:43
|
作者
Sun, Haijun [1 ,6 ]
Zhang, Yu [1 ]
Yang, Yiting [1 ]
Chen, Yudong [2 ]
Jeyakumar, Paramsothy [3 ]
Shao, Qianlan [1 ]
Zhou, Youfeng [1 ]
Ma, Meng [1 ]
Zhu, Ruiqi [1 ]
Qian, Qiawei [1 ]
Fan, Yuerong [1 ]
Xiang, Shujie [1 ]
Zhai, Ningning [1 ]
Li, Yifan [1 ]
Zhao, Qingfeng [4 ]
Wang, Hailong [5 ]
机构
[1] Nanjing Forestry Univ, Coll Forestry, Coinnovat Ctr Sustainable Forestry Southern China, Nanjing 210037, Peoples R China
[2] Minist Ecol Environm, Nanjing Inst Environm Sci, Nanjing 210042, Peoples R China
[3] Massey Univ, Sch Agr & Environm, Environm Sci, Private Bag 11 222, Palmerston North 4442, New Zealand
[4] Shandong Qihong Biol Technol Co Ltd, Weifang 262400, Shandong, Peoples R China
[5] Foshan Univ, Sch Environm & Chem Engn, Foshan 528000, Peoples R China
[6] Nanjing Forestry Univ, Key Lab Soil & Water Conservat & Ecol Restorat Ji, Nanjing 210037, Peoples R China
基金
中国国家自然科学基金;
关键词
Atmospheric environment; Biochar; Global climate change; Nitrogen management; Soil quality; BIOORGANIC FERTILIZER; LEACHING LOSSES; N2O EMISSIONS; NH3; MICROBIOME; ECOSYSTEMS; UREA;
D O I
10.1016/j.envpol.2021.116640
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Biofertilizer can improve soil quality, especially the microbiome composition, which potentially affect soil nitrogen (N) cycling. However, little is known about the responses of nitrous oxide (N2O) emission and ammonia (NH3) volatilization from biochar-amended paddy soil to the biofertilizer application. Therefore, we conducted a soil column experiment using four 240 kg N ha(-1) (equivalent to 1.7 g N pot(-1)) treatments consisting of biofertilizer (3 t ha(-1), equivalent to 21.2 g pot(-1)), biochar (7.5 t ha(-1), equivalent to 63.6 g pot(-1)), and a mixture of biofertilizer and biochar at the same rate and a control (CK). The results showed that the N2O emissions and NH3 volatilizations were equivalent to 0.15-0.28% and 18.0-31.5% of rice seasonal N applied to the four treatments, respectively. Two treatments with biofertilizer and biochar individual amendment significantly increased (P < 0.05) the N2O emissions to same degree by 30.2%, while co-application of biochar and biofertilizer further increased the N2O emission by 74.4% compared to the control. The higher N2O emission was likely attributed to the increased gene copies of AOA, nirK, and nirS. Applying biofertilizer significantly increased (P < 0.05) NH3 volatilization by 24.7% relative to the control, while applying biochar had no influence on NH3 volatilization. Co-application of biofertilizer and biochar significantly decreased (P < 0.05) NH3 volatilization by 12.3% compared to the control. Overall, the net global warming potential based on NH3 and N2O in current study increased by 13.0-26.0% in both the individual- and co-application of biofertilizer and biochar. Interestingly, both individual- and co-applications of biofertilizer and biochar increased the rice grain yield by 16.5-38.3%. Therefore, applications of biofertilizer and biochar did not increase the GHGI. Particularly, the co-applying of them significantly lowered (P < 0.05) the GHGI by 15.2%. In conclusion, biofertilizer and biochar should be co-applied to achieve the goals of environment protection and food security. (C) 2021 Elsevier Ltd. All rights reserved.
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页数:9
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