Author
Listed:
- Hongyuan Liu
(National Key Laboratory of Efficient Utilization of Nutrient Resources, Shandong Academy of Agricultural Sciences, Jinan 250100, China
National Technological Innovation Center for Comprehensive Utilization of Saline-Alkali Land, Dongying 257347, China)
- Nana Wang
(National Key Laboratory of Efficient Utilization of Nutrient Resources, Shandong Academy of Agricultural Sciences, Jinan 250100, China
National Technological Innovation Center for Comprehensive Utilization of Saline-Alkali Land, Dongying 257347, China)
- Yanjun Wang
(National Key Laboratory of Efficient Utilization of Nutrient Resources, Shandong Academy of Agricultural Sciences, Jinan 250100, China
National Technological Innovation Center for Comprehensive Utilization of Saline-Alkali Land, Dongying 257347, China)
- Ying Li
(National Key Laboratory of Efficient Utilization of Nutrient Resources, Shandong Academy of Agricultural Sciences, Jinan 250100, China
National Technological Innovation Center for Comprehensive Utilization of Saline-Alkali Land, Dongying 257347, China)
- Yan Zhang
(National Key Laboratory of Efficient Utilization of Nutrient Resources, Shandong Academy of Agricultural Sciences, Jinan 250100, China
National Technological Innovation Center for Comprehensive Utilization of Saline-Alkali Land, Dongying 257347, China)
- Gaoxiang Qi
(National Key Laboratory of Efficient Utilization of Nutrient Resources, Shandong Academy of Agricultural Sciences, Jinan 250100, China
National Technological Innovation Center for Comprehensive Utilization of Saline-Alkali Land, Dongying 257347, China)
- Hongyun Dong
(National Key Laboratory of Efficient Utilization of Nutrient Resources, Shandong Academy of Agricultural Sciences, Jinan 250100, China
National Technological Innovation Center for Comprehensive Utilization of Saline-Alkali Land, Dongying 257347, China)
- Hongcheng Wang
(National Key Laboratory of Efficient Utilization of Nutrient Resources, Shandong Academy of Agricultural Sciences, Jinan 250100, China
National Technological Innovation Center for Comprehensive Utilization of Saline-Alkali Land, Dongying 257347, China)
- Xijin Zhang
(National Key Laboratory of Efficient Utilization of Nutrient Resources, Shandong Academy of Agricultural Sciences, Jinan 250100, China
National Technological Innovation Center for Comprehensive Utilization of Saline-Alkali Land, Dongying 257347, China)
- Xinhua Li
(National Key Laboratory of Efficient Utilization of Nutrient Resources, Shandong Academy of Agricultural Sciences, Jinan 250100, China
National Technological Innovation Center for Comprehensive Utilization of Saline-Alkali Land, Dongying 257347, China)
Abstract
Biochar application is considered an effective method for reducing nitrous oxide (N 2 O) emissions from soil. However, the mechanisms underlying the influence of various biochar dosages on soil N 2 O emissions and the duration of one-time biochar application remain unclear. The effects of different biochar application rates and a one-time application on soil N 2 O emissions in the Huanghuaihai Plain of China were investigated through a field experiment from 2020 to 2022. In the wheat and maize rotation system, six treatments were administered: no biochar (C0); 2 (C1), 4 (C2), 8 (C3), and 12 t/hm 2 biochar (C4) applied annually; and a one-time application of 12 t/hm 2 biochar (CS) in 2018. Our results indicate that, compared with C0, biochar significantly inhibited soil N 2 O emissions, particularly in the C3 and C4 treatments, with reductions of 31.36–56.21% and 36.92–52.45%, respectively. However, CS did not significantly affect soil N 2 O emissions during the study period. These findings suggest that the biochar’s inhibitory effect on soil N 2 O emissions is contingent upon the dosage and frequency of application. A structural equation model revealed that biochar decreases soil N 2 O emissions by enhancing the reduction in N 2 O during denitrification. Under the conditions of this experiment, based on a logistic ecological model, a one-time application of 12 t/hm 2 biochar was projected to significantly reduce soil N 2 O emissions for approximately 1.77 years. On the whole, biochar reduces soil N 2 O emissions mainly by regulating N 2 O production through denitrification, and the duration of this inhibition of N 2 O emissions mainly depends on the application amount and frequency of biochar application.
Suggested Citation
Hongyuan Liu & Nana Wang & Yanjun Wang & Ying Li & Yan Zhang & Gaoxiang Qi & Hongyun Dong & Hongcheng Wang & Xijin Zhang & Xinhua Li, 2024.
"Inhibitory Effects of Biochar on N 2 O Emissions through Soil Denitrification in Huanghuaihai Plain of China and Estimation of Influence Time,"
Sustainability, MDPI, vol. 16(13), pages 1-18, July.
Handle:
RePEc:gam:jsusta:v:16:y:2024:i:13:p:5813-:d:1431106
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