Open AccessEffects of biochar application on soil nitrogen transformation, microbial functional genes, enzyme activity, and plant nitrogen uptake: A meta‐analysis of field studies
Author(s) -
Zhang Leiyi,
Jing Yiming,
Chen Chengrong,
Xiang Yangzhou,
Rezaei Rashti Mehran,
Li Yantao,
Deng Qi,
Zhang Renduo
Publication year - 2021
Publication title -
gcb bioenergy
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 1.378
H-Index - 63
eISSN - 1757-1707
pISSN - 1757-1693
DOI - 10.1111/gcbb.12898
Subject(s) - biochar , nitrification , denitrifying bacteria , nitrogen cycle , mineralization (soil science) , leaching (pedology) , nitrogen fixation , nitrogen , chemistry , environmental chemistry , agronomy , denitrification , soil ph , soil water , biology , ecology , organic chemistry , pyrolysis
Biochar application can influence soil nitrogen (N) cycle through biological and abiotic processes. However, studies on comprehensive examination of the effects of biochar application on microbially mediated N‐cycling processes (N mineralization, nitrification, denitrification, and fixation) and soil N fate (i.e., plant N uptake, soil N 2 O emission, and N leaching) are warranted. Therefore, the aim of this study was to examine the effects of biochar application on soil N transformation, microbial functional gene abundance, enzyme activity, and plant N uptake. To achieve the objective of this study, a meta‐analysis involving 131 peer‐reviewed field experiments was conducted. Results showed that field application of biochar significantly enhanced soil NH 4 + and NO 3 ‐ content, N mineralization, nitrification, N 2 fixation, and plant N uptake by 5.3%, 3.7%, 15.3%, 48.5%, 14.7%, and 18.3%, respectively, but reduced N 2 O emissions and N leaching by 14.9% and 10.9%, respectively. Biochar application also increased the abundance of soil denitrifying/nitrifying genes ( amoA , narG , nirS / nirK + S , and nosZ ), proportion of N 2 fixation bacteria, and N‐acetyl‐glucosaminidase activity by 18.6%–87.6%. Soil NO 3 ‐ content was positively correlated with AOA ‐ amoA abundance, and soil N 2 O emission was positively correlated with the relative abundance of genes (e.g., amoA , narG , and nirS / nirK ) involved in N 2 O production. Furthermore, long‐term biochar application tended to increase AOB ‐ amoA and nirK + S abundance, especially soil N 2 O emission and N leaching. Overall, the findings of this study indicated that biochar application accelerated microbially mediated N‐cycling processes under field conditions, thereby enhancing soil N availability and plant productivity. However, long‐term biochar application may increase N losses. Therefore, future studies should be conducted to examine the effect of long‐term biochar application on the soil N cycle and the underlying microbial mechanisms.