Yongshan Li

Prof. Dr. Yongshan Li

orcid

Research Focus & Metrics

Academic Career Length

21Years (2006-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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18 April 2018 in PLOS ONE
Verified
Journal Article
Open access
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JLJing Li
Jing Li
XWXueping Wu
Xueping Wu
MGMesfin Tsegaye Gebremikael
Mesfin Tsegaye Gebremikael
HWHuijun Wu
Huijun Wu
DCDianxiong Cai
Dianxiong Cai
JXJilong Xi
Jilong Xi
Microbial mechanisms associated with soil organic carbon (SOC) decomposition are poorly understood. We aim to determine the effects of inorganic and organic fertilizers on soil labile carbon (C) pools, microbial community structure and C mineralization rate under an intensive wheat-maize double cropping system in Northern China. Soil samples in 0–10 cm layer were collected from a nine-year field trial involved four treatments: no fertilizer, CK; nitrogen (N) and phosphorus (P) fertilizers, NP; maize straw combined with NP fertilizers, NPS; and manure plus straw and NP fertilizers, NPSM. Soil samples were analyzed to determine labile C pools (including dissolved organic C, DOC; light free organic C, LFOC; and microbial biomass C, MBC), microbial community composition (using phospholipid fatty acid (PLFA) profiles) and SOC mineralization rate (from a 124-day incubation experiment). This study demonstrated that the application of chemical fertilizers (NP) alone did not alter labile C fractions, soil microbial communities and SOC mineralization rate from those observed in the CK treatment. Whereas the use of straw in conjunction with chemical fertilizers (NPS) became an additional labile substrate supply that decreased C limitation, stimulated growth of all PLFA-related microbial communities, and resulted in 53% higher cumulative mineralization of C compared to that of CK. The SOC and its labile fractions explained 78.7% of the variance of microbial community structure. Further addition of manure on the top of straw in the NPSM treatment did not significantly increase microbial community abundances, but it did alter microbial community structure by increasing G+/G- ratio compared to that of NPS. The cumulative mineralization of C was 85% higher under NPSM fertilization compared to that of CK. Particularly, the NPSM treatment increased the mineralization rate of the resistant pool. This has to be carefully taken into account when setting realistic and effective goals for long-term soil C stabilization.

1 April 2007 in Soil and Tillage Research
Verified
Journal Article
Closed access
YLYongshan Li
Yongshan Li
LWLiang-Huan Wu
Liang-Huan Wu
LZLi-Mei Zhao
Li-Mei Zhao
XLXing-Hua Lu
Xing-Hua Lu
QFQiao-Lan Fan
Qiao-Lan Fan
FZFu-Suo Zhang
Fu-Suo Zhang

1 January 2009 in Experimental Agriculture
Verified
Journal Article
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LZLimei Zhao
Limei Zhao
LWLianghuan Wu
Lianghuan Wu
YLYongshan Li
Yongshan Li
XLXinghua Lu
Xinghua Lu
DZDefeng Zhu
Defeng Zhu
NUNorman Uphoff
Norman Uphoff
SUMMARY: Field experiments were conducted in 2005 and 2006 to investigate the impacts of alternative rice cultivation systems on grain yield, water productivity, N uptake and N use efficiency (ANUE, agronomic N use efficiency; PFP, partial factor productivity of applied N). The trials compared the practices used with the system of rice intensification (SRI) and traditional flooding (TF). The effects of different N application rates (0, 80, 160 and 240 kg ha−1) and of N rates interacting with the cultivation system were also evaluated. Resulting grain yields with SRI ranged from 5.6 to 7.3 t ha−1, and from 4.1 to 6.4 t ha−1 under TF management. On average, grain yields under SRI were 21% higher in 2005 and 22% higher in 2006 than with TF. Compared with TF, SRI plots had higher harvest index across four fertilizer N rates in both years. However, there was no significance difference in above-ground biomass between two cultivation systems in either year. ANUE was increased significantly under SRI at 80 kg N ha−1 compared with TF, while at higher N application rates, ANUE with SRI was significantly lower than TF. Compared with TF, PFP under SRI was higher across all four N rates in both years, although the difference at 240 kg N ha−1 was not significant. As N rate increased, the ANUE and PFP under both SRI and TF significantly decreased. Reduction in irrigation water use with SRI was 40% in 2005 and 47% in 2006, and water use efficiency, both total and from irrigation, were significantly increased compared to TF. With both SRI and TF, the highest N application was associated with decreases in grain yield, N use efficiency and water use efficiency. This is an important finding given current debates whether N application rates in China are above the optimum, especially considering consequences for soil and water resources. Cultivation system, N rates and their interactions all produced significant differences in this study. Results confirmed that optimizing fertilizer N application rates under SRI is important to increase yield, N use efficiency and water use efficiency.

7 January 2010 in Communications in Soil Science and Plant Analysis
Verified
Journal Article
Closed access
LZLimei Zhao
Limei Zhao
LWLianghuan Wu
Lianghuan Wu
YLYongshan Li
Yongshan Li
SASarkar Animesh
Sarkar Animesh
DZDefeng Zhu
Defeng Zhu
NUNorman Uphoff
Norman Uphoff
To compare the effects of the system of rice intensification (SRI) on yield, water use efficiency, and microbial biomass in associated rice soils, a field experiment was conducted in 2004 at the Agriculture Experimental Farm of Zhejiang University in Zhejiang Province, China. The treatments evaluated were traditional flooding (TF) vs. SRI cultivation methods. Grain yield in the SRI treatment was 26.4% greater than that in the TF treatment, reducing water use by 461.5 mm. Compared to TF, SRI increased water use efficiency by 91.3% and irrigation water use efficiency by 194.9%. Soil microbial indicators during the rice‐growing season also diverged between TF and SRI. Microbial biomass C (MBC) was in the range of 101–196 mg kg−1 for TF vs. 113–224 mg kg−1 for SRI; microbial biomass N (MBN) was in the range of 14–33 mg kg−1 for TF vs. 28–53 mg kg−1 in SRI. Compared to TF, SRI significantly increased both MBC and MBN, regardless of sampling date.

18 February 2011 in Paddy and Water Environment
Verified
Journal Article
Closed access
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LZLimei Zhao
Limei Zhao
LWLianghuan Wu
Lianghuan Wu
MWMeiyan Wu
Meiyan Wu
YLYongshan Li
Yongshan Li

4 December 2006 in Journal of the Science of Food and Agriculture
Verified
Journal Article
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XLXinghua Lu
Xinghua Lu
LWLianghuan Wu
Lianghuan Wu
LPlinjiang pang
linjiang pang
YLYongshan Li
Yongshan Li
JWJianguo Wu
Jianguo Wu
Fusuo ZhangFusuo Zhang
Fusuo Zhang