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长期施肥下三种典型农田土壤土壤Olsen-P 对磷收支的响应。

The response of soil Olsen-P to the P budgets of three typical cropland soil types under long-term fertilization.

机构信息

Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences/National Engineering Laboratory for Improving Quality of Arable Land, Beijing, P. R. China.

Guangdong Provincial Bioengineering Institute (Guangzhou Sugarcane Industry Research Institute)/Guangdong Key Laboratory of Sugarcane Improvement and Biorefinery, Guangzhou, P. R. China.

出版信息

PLoS One. 2020 Mar 18;15(3):e0230178. doi: 10.1371/journal.pone.0230178. eCollection 2020.

Abstract

The Olsen phosphorus (Olsen-P) concentration of soil is generally a good indicator for estimating the bioavailability of P and environmental risk in soils. To maintain soil Olsen-P at adequate levels for crop growth and environmental sustainability, the relationship between soil Olsen-P and the P budget (the P input minus the output) as well as the variations of soil Olsen-P and P budget were investigated from three long-term (22 years) experiments in China. Five treatments were selected: (1) unfertilized control (CK); (2) nitrogen and potassium (NK); (3) nitrogen, phosphorous, and potassium (NPK); (4) nitrogen, phosphorous, potassium and straw; (5) nitrogen, phosphorous, potassium and manure. The results showed that without P fertilizers (CK, NK), there was a soil P deficit of 75-640 kg ha-1, and the lowest P deficit (mean of CK and NK) was in Eutric Cambisol. Soil Olsen-P decreased by 0.11-0.39 mg kg-1 year-1 in the order of Luvic Phaeozems > Eutric Cambisol > Calcaric Cambisol. Soil Olsen-P and the P deficit had a significantly (P<0.01) positive linear relationship. For every 100 kg of P ha-1 of deficit, soil Olsen-P decreased by 0.44-9.19 mg kg-1 in the order of Eutric Cambisol > Luvic Phaeozems > Calcaric Cambisol. Under the P fertilizer treatments (NPK, NPKS, and NPKM), soil Olsen-P showed an obvious surplus (except the NPK and NPKS in Luvic Phaeozems) of 122-2190 kg ha-1, and the largest P surplus was found under the NPKM treatment at each site. The relation between soil Olsen-P and the experimental years could be simulated using quadratic equation of one unknown in Calcaric Cambisol for the lower P input after 14 years of fertilization. And soil Olsen-P increased by 1.30-7.69 mg kg-1 year-1 in the order of Luvic Phaeozems > Eutric Cambisol. The relation between soil Olsen-P and the P surplus could be simulated by a simple linear equation except under NPK and NPKS in Luvic Phaeozems. With 100 kg ha-1 P surplus, soil Olsen-P increased by 3.24-7.27 mg kg-1 in the order of Calcaric Cambisol (6.42 mg kg-1) > Eutric Cambisol (3.24 mg kg-1). In addition, the change in soil Olsen-P with a 100 kg P ha-1 surplus (soil Olsen-P efficiency) was affected by the soil organic matter (SOM), pH, and CaCO3 content, etc. In the practice of fertilization, it's not necessary to increase the amount of P fertilizers, farmers should take measure to solve the local problem, for adjust the soil pH of Eutric Cambisol and Calcaric Cambisol, and apply more nitrogen in Luvic Phaeozems. In the area of serious soil P surplus, it is encouraged to stop applying P fertilizers for a few years to take advantage of soil accumulated P and make the high Olsen-P content decrease to a reasonable level.

摘要

土壤奥尔森磷(Olsen-P)浓度通常是评估土壤磷生物有效性和环境风险的良好指标。为了维持土壤奥尔森磷水平以满足作物生长和环境可持续性的需要,研究了中国三个长期(22 年)试验中的土壤奥尔森磷与磷预算(磷输入减去输出)之间的关系以及土壤奥尔森磷和磷预算的变化。选择了五种处理方式:(1)不施肥对照(CK);(2)氮钾(NK);(3)氮磷钾(NPK);(4)氮磷钾和秸秆;(5)氮磷钾和粪肥。结果表明,在不施磷肥的情况下(CK、NK),土壤存在 75-640 kg ha-1 的磷亏缺,亏缺最低的是潴育性水稻土。土壤奥尔森磷每年减少 0.11-0.39 mg kg-1,顺序为暗棕壤>潴育性水稻土>钙积性水稻土。土壤奥尔森磷与磷亏缺呈显著(P<0.01)正线性关系。每亏缺 100 kg P ha-1,土壤奥尔森磷减少 0.44-9.19 mg kg-1,顺序为潴育性水稻土>暗棕壤>钙积性水稻土。在施磷肥处理(NPK、NPKS 和 NPKM)下,土壤奥尔森磷表现出明显的盈余(暗棕壤中的 NPK 和 NPKS 除外),为 122-2190 kg ha-1,每个地点的 NPKM 处理下盈余最大。在施磷 14 年后,土壤奥尔森磷与试验年限的关系可以用一元二次方程来模拟,钙积性水稻土的磷输入较低。土壤奥尔森磷每年增加 1.30-7.69 mg kg-1,顺序为暗棕壤>潴育性水稻土。除了暗棕壤中的 NPK 和 NPKS 之外,土壤奥尔森磷与磷盈余的关系可以用简单线性方程来模拟。每盈余 100 kg P ha-1,土壤奥尔森磷增加 3.24-7.27 mg kg-1,顺序为钙积性水稻土(6.42 mg kg-1)>潴育性水稻土(3.24 mg kg-1)。此外,土壤奥尔森磷的变化量(土壤奥尔森磷效率)受土壤有机质(SOM)、pH 值和碳酸钙含量等因素的影响。在施肥实践中,没有必要增加磷肥的用量,农民应采取措施解决当地的问题,调节钙积性水稻土和潴育性水稻土的 pH 值,并在暗棕壤中施更多的氮。在土壤磷严重盈余的地区,建议停止施磷几年,利用土壤积累的磷,使高奥尔森磷含量降低到合理水平。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12e1/7080265/866c01c3d319/pone.0230178.g001.jpg

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