Graduate School of Agriculture, Hokkaido University , Sapporo 060-8589, Japan.
School of Agriculture and Biology, Shanghai Jiaotong University , 200240 Shanghai, China.
J Agric Food Chem. 2017 Apr 19;65(15):3085-3095. doi: 10.1021/acs.jafc.6b05813. Epub 2017 Apr 10.
To characterize the dynamic mobilization of heavy metals (HM) in a crop-soil system affected by cattle manure (CM) application, soybean [Glycine max L. Merr. cv. Toyoharuka] crops were exposed in a chronological pot experiment to three CM application rates and sampled at two vegetative stages and two reproductive stages. A sequential extraction procedure for metal fractionation, soil pH, microbial activity, and plant HM uptake was determined. In non-rhizopshere soil, with CM application a liming effect was detected, and increased microbial activity was detected at the reproductive stage. CM application shifted Cd from available state to oxide-bound pool in non-rhizosphere soil; however, shifts in Cd from an oxide-bound pool to the available state were observed in rhizosphere soil. CM application stabilized the available Zn and Pb to oxide-bound Zn and organic-bound Pb in both non-rhizosphere and rhizosphere soils, and the stabilizing degree increased with higher CM application rates. The promoted Zn immobilization in the rhizosphere was due to the liming effects induced by added CM that counteracted the root-induced acidification. On the basis of a stepwise multiple regression analysis, the shift of Cd and Pb fractionation was mainly related to microbial activity. Adding manure inhibited Zn and Pb uptake but promoted Cd uptake by soybean, and a greater influence was detected at the reproductive stage, at which CM application increased the root Cd-absorbing power but did not significantly affect the Zn- and Pb-absorbing powers. In an agricultural context, long-term CM application, even at the recommended rate of 10.13 Mg ha, may cause a soybean Zn deficiency and high Pb accumulation in Haplic Fluvisols, although CM is often considered as an environmentally friendly fertilizer.
为了描述受牛粪(CM)施用影响的作物-土壤系统中重金属(HM)的动态迁移,在一项时间顺序的盆栽实验中,将大豆[Glycine max L. Merr. cv. Toyoharuka]作物暴露于三种 CM 施用量,并在两个营养阶段和两个生殖阶段进行采样。采用金属形态分级、土壤 pH 值、微生物活性和植物 HM 吸收的顺序提取程序进行了测定。在非根际土壤中,随着 CM 的施用,发现有石灰化作用,并且在生殖阶段检测到微生物活性增加。CM 施用将 Cd 从可利用状态转移到非根际土壤中的氧化物结合态;然而,在根际土壤中观察到 Cd 从氧化物结合态向可利用状态的转移。CM 施用将可利用的 Zn 和 Pb 稳定在非根际和根际土壤中的氧化物结合 Zn 和有机结合 Pb 中,并且随着 CM 施用量的增加,稳定程度增加。根际中 Zn 的固定化增强是由于添加的 CM 诱导的石灰化作用抵消了根诱导的酸化。基于逐步多元回归分析,Cd 和 Pb 形态的变化主要与微生物活性有关。施用有机肥抑制了大豆对 Zn 和 Pb 的吸收,但促进了 Cd 的吸收,在生殖阶段的影响更大,此时 CM 施用增加了根对 Cd 的吸收能力,但对 Zn 和 Pb 的吸收能力没有显著影响。在农业背景下,即使按照建议的 10.13 Mg ha 的施用量长期施用 CM,也可能导致在 Haplic Fluvisols 中大豆缺锌和 Pb 积累量高,尽管 CM 通常被认为是一种环保型肥料。