Reductive soil disinfestation promotes vegetable N uptake by regulating soil gross N transformation and improving the quality of degraded soil

被引:5
|
作者
Dan, Xiaoqian [1 ]
He, Mengqiu [1 ]
Chen, Shending [1 ]
He, Xiaoxiang [1 ]
Zhao, Chang [1 ]
Meng, Lei [2 ]
Cai, Zucong [1 ]
Zhang, Jinbo [1 ,2 ,3 ,4 ]
Mueller, Christoph [5 ,6 ]
机构
[1] Nanjing Normal Univ, Sch Geog, Nanjing 210023, Peoples R China
[2] Hainan Univ, Coll Trop Crops, Haikou 570228, Hainan, Peoples R China
[3] Jiangsu Ctr Collaborat Innovat Geog Informat Reso, Nanjing 210023, Peoples R China
[4] Jiangsu Engn Res Ctr Soil Utilizat & Sustainable, Nanjing 210023, Peoples R China
[5] Justus Liebig Univ Giessen, Inst Plant Ecol, Heinrich Buff Ring 26, D-35392 Giessen, Germany
[6] Univ Coll Dublin, Sch Biol & Environm Sci, Earth Inst, Dublin, Ireland
基金
中国国家自然科学基金;
关键词
Reductive soil disinfestation; Vegetable N uptake; Gross N transformation rates; Degraded vegetable soil; N-15; tracing; PLANT-PARASITIC NEMATODES; BIOLOGICAL-CONTROL; NITROGEN-BALANCE; CROPPING SYSTEMS; NITRIFICATION; MICROORGANISMS; AMENDMENTS; RESPONSES; MONOCULTURE; COMPETITION;
D O I
10.1007/s11104-022-05683-z
中图分类号
S3 [农学(农艺学)];
学科分类号
0901 ;
摘要
Purpose Reductive soil disinfestation (RSD) has been widely applied to improve soil degradation, enhancing vegetable N uptake and productivity. However, its effects on interactions between vegetable N uptake and soil gross N transformation remain unclear. Methods Two degraded vegetable soils were treated with RSD and N-15 tracing pot experiments were conducted to quantify the effects of RSD on N cycling in vegetable-soil systems. Results Vegetable NH4+ and NO3- uptake rates were 1.0-6.5 times higher following RSD than CK, while soil gross N mineralization rates (M) ranged from 0.83-13.00 mg N kg(-1) d(-1), and were significantly higher than the CK (0.21-8.71 mg N kg(-1) d(-1)). Meanwhile, autotropic nitrification rate (O-NH4) increased by 1.7-4.2 following RSD, while NH4+ immobilization rates (I-NH4) were significantly inhibited by RSD in the presence of planting. This induced a decrease in (O-NH4 + I-NH4)/M, and increases in NH4+ retention times and production rates of soil NO3- following RSD. In addition, RSD improved the overall quality of the degraded soils (increasing the pH, and decreasing EC and NO3- contents as well as pathogen abundance), further promoting vegetable N uptake. Conclusion RSD promoted vegetable N uptake by regulating soil gross N transformation rates and improving the quality of degraded vegetable soil. However, NO3- production rates were enhanced following RSD, increasing the risk of NO3- leaching and gaseous N losses. N fertilizer management under RSD therefore requires further attention.
引用
收藏
页码:147 / 160
页数:14
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