Details
Original language | English |
---|---|
Article number | 106029 |
Journal | CATENA |
Volume | 211 |
Publication status | Published - Apr 2022 |
Externally published | Yes |
Abstract
Land-use changes could potentially exert a strong influence on soil quality and soil microbial communities. Moreover, microbial taxa are also important drivers of soil ecological functions. However, the linkage between soil quality and soil microbial communities is in need of deeper understanding. Here, we examined the effects of soil fertility quality on microbial community structure that identified by pyrosequencing and functions that predicted by the FAPROTAX functional annotations dataset after forest conversion to vegetable cropland and tea plantations. Soil quality index was significantly increased after natural forest (0.2) conversion to vegetable cropland (0.7) and tea plantations (0.3–0.6). Soil bacterial beta diversity significantly correlated to soil quality index, but the sensitivity of individual microbial groups varied in response to changes in soil quality. Higher soil quality promoted bacterial diversity in vegetable cropland but decreased it in tea plantations, which implied soil quality was a structural factor in bacterial community composition but had contrasting effects for croplands versus plantations. Agricultural management played a negative role in maintaining microbial interactions, as identified by the network analysis, and furthermore the analysis revealed key functions of the microbial communities. After land-use change, the abundance (e.g., level, intensity) of microbial groups involved in N-cycling increased in tea plantations but decreased in vegetable cropland. The abundance of microbes involved in C-cycling featured an opposite trend. Higher level of N-fixation in tea plantations but the higher abundance of N-oxidation in vegetable cropland was demonstrated. Higher abundance of ammonia-oxidizing bacteria (8.5 × 104 vs. 0.9–2.4 × 104 copies) and ammonia-oxidizing archaea (3.0 × 105 vs. 0.5–1.0 × 105 copies) as identified by qPCR in cropland than that in plantations corroborated the FAPROTAX prediction. Therefore, the key taxa of soil microbial communities and microbial functions were largely dependent on changes in soil quality and determined responses to specific agricultural management.
Keywords
- Agricultural management, C and N cycling, Co-occurrence network, Fertility, Land-use change, Microbial diversity, Soil quality
ASJC Scopus subject areas
- Earth and Planetary Sciences(all)
- Earth-Surface Processes
Sustainable Development Goals
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In: CATENA, Vol. 211, 106029, 04.2022.
Research output: Contribution to journal › Article › Research › peer review
}
TY - JOUR
T1 - Enhanced soil quality after forest conversion to vegetable cropland and tea plantations has contrasting effects on soil microbial structure and functions
AU - Fan, Lichao
AU - Shao, Guodong
AU - Pang, Yinghua
AU - Dai, Hongcui
AU - Zhang, Lan
AU - Yan, Peng
AU - Zou, Zhenhao
AU - Zhang, Zheng
AU - Xu, Jianchu
AU - Zamanian, Kazem
AU - Dorodnikov, Maxim
AU - Li, Xin
AU - Gui, Heng
AU - Han, Wenyan
N1 - Funding information: This research was supported by the National Key R&D Program of China (2017YFE0107500). Heng Gui would like to thank the support from the National Natural Science of China (NSFC Grant number: 32001296). Kazem Zamanian would like to thank the Research Fund for International Young Scientists of National Natural Science of China to K.Z. (Grant number: 42050410320). Funding for study abroad program by the government of Shandong Province for financial support for Dr. Hongcui Dai
PY - 2022/4
Y1 - 2022/4
N2 - Land-use changes could potentially exert a strong influence on soil quality and soil microbial communities. Moreover, microbial taxa are also important drivers of soil ecological functions. However, the linkage between soil quality and soil microbial communities is in need of deeper understanding. Here, we examined the effects of soil fertility quality on microbial community structure that identified by pyrosequencing and functions that predicted by the FAPROTAX functional annotations dataset after forest conversion to vegetable cropland and tea plantations. Soil quality index was significantly increased after natural forest (0.2) conversion to vegetable cropland (0.7) and tea plantations (0.3–0.6). Soil bacterial beta diversity significantly correlated to soil quality index, but the sensitivity of individual microbial groups varied in response to changes in soil quality. Higher soil quality promoted bacterial diversity in vegetable cropland but decreased it in tea plantations, which implied soil quality was a structural factor in bacterial community composition but had contrasting effects for croplands versus plantations. Agricultural management played a negative role in maintaining microbial interactions, as identified by the network analysis, and furthermore the analysis revealed key functions of the microbial communities. After land-use change, the abundance (e.g., level, intensity) of microbial groups involved in N-cycling increased in tea plantations but decreased in vegetable cropland. The abundance of microbes involved in C-cycling featured an opposite trend. Higher level of N-fixation in tea plantations but the higher abundance of N-oxidation in vegetable cropland was demonstrated. Higher abundance of ammonia-oxidizing bacteria (8.5 × 104 vs. 0.9–2.4 × 104 copies) and ammonia-oxidizing archaea (3.0 × 105 vs. 0.5–1.0 × 105 copies) as identified by qPCR in cropland than that in plantations corroborated the FAPROTAX prediction. Therefore, the key taxa of soil microbial communities and microbial functions were largely dependent on changes in soil quality and determined responses to specific agricultural management.
AB - Land-use changes could potentially exert a strong influence on soil quality and soil microbial communities. Moreover, microbial taxa are also important drivers of soil ecological functions. However, the linkage between soil quality and soil microbial communities is in need of deeper understanding. Here, we examined the effects of soil fertility quality on microbial community structure that identified by pyrosequencing and functions that predicted by the FAPROTAX functional annotations dataset after forest conversion to vegetable cropland and tea plantations. Soil quality index was significantly increased after natural forest (0.2) conversion to vegetable cropland (0.7) and tea plantations (0.3–0.6). Soil bacterial beta diversity significantly correlated to soil quality index, but the sensitivity of individual microbial groups varied in response to changes in soil quality. Higher soil quality promoted bacterial diversity in vegetable cropland but decreased it in tea plantations, which implied soil quality was a structural factor in bacterial community composition but had contrasting effects for croplands versus plantations. Agricultural management played a negative role in maintaining microbial interactions, as identified by the network analysis, and furthermore the analysis revealed key functions of the microbial communities. After land-use change, the abundance (e.g., level, intensity) of microbial groups involved in N-cycling increased in tea plantations but decreased in vegetable cropland. The abundance of microbes involved in C-cycling featured an opposite trend. Higher level of N-fixation in tea plantations but the higher abundance of N-oxidation in vegetable cropland was demonstrated. Higher abundance of ammonia-oxidizing bacteria (8.5 × 104 vs. 0.9–2.4 × 104 copies) and ammonia-oxidizing archaea (3.0 × 105 vs. 0.5–1.0 × 105 copies) as identified by qPCR in cropland than that in plantations corroborated the FAPROTAX prediction. Therefore, the key taxa of soil microbial communities and microbial functions were largely dependent on changes in soil quality and determined responses to specific agricultural management.
KW - Agricultural management
KW - C and N cycling
KW - Co-occurrence network
KW - Fertility
KW - Land-use change
KW - Microbial diversity
KW - Soil quality
UR - http://www.scopus.com/inward/record.url?scp=85122667838&partnerID=8YFLogxK
U2 - 10.1016/j.catena.2022.106029
DO - 10.1016/j.catena.2022.106029
M3 - Article
AN - SCOPUS:85122667838
VL - 211
JO - CATENA
JF - CATENA
SN - 0341-8162
M1 - 106029
ER -