Laboratoire d'Etudes des Transferts en Hydrologie et Environnement, LTHE, UMR 5564, CNRS-INSU/Univ. Grenoble I/INPG/IRD, 1025 rue de la Piscine, Domaine Universitaire BP53, 38041 Grenoble Cedex 9, France.
Sci Total Environ. 2014 Jan 1;466-467:681-9. doi: 10.1016/j.scitotenv.2013.07.064. Epub 2013 Aug 19.
In this study we evaluated the effect of the long term organic management of a vineyard-soil on the biogeochemistry of copper at the micro-aggregate scale. The model vineyard-soil (Mâcon-France) experienced a long-term field-experiment that consisted in amendments and vegetations with various materials and plants. We studied specifically the effect of Straw (S) and Conifer Compost (CC) organic amendments and Clover (Cl) and Fescue (F) vegetation on the fate of copper (fungicide) in the surface layer of this loamy soil, through a comparison with the Non Amended soil (NA). After collection the five soils were immediately physically fractionated in order to obtain 5 granulometric size-fractions. All soils and size-fractions were quantitatively characterized in terms of granulometry, chemical content and copper distribution, speciation and bioavailability to bacteria and plants. The results showed strong increases of soil-constituents aggregation for all treatments (Cl>CC>S>F>NA), in relation with the increased cementation of soil-constituents by organic matter (OM). The distribution patterns of all major elements and organic carbon were found highly variable within the soil sub-fractions and also between the 5 treatments. Due to their specific inorganic and organic composition, soil sub-fractions can thus be considered as a specific microbial habitat. Added OM accumulated preferentially in the 20-2 μm and in the >250 μm of the 5 soils. The distribution patterns of copper as well as its speciation and bioavailability to bacteria in the soil sub-fractions were shown to be strongly different among the five soils, in relation with OM distribution. Our results also suggest that Cu-bioavailability to plants is controlled by soil-rhizosphere structure. Altogether our results permitted to show that long-term organic management of a vineyard soil induced stable modifications of soil physical and chemical properties at both macro and micro-scales. These modifications affected in turn the micro-scale biogeochemistry of copper, and especially its bioavailability to bacteria and plants.
在这项研究中,我们评估了葡萄园土壤的长期有机管理对铜的生物地球化学在微团聚体尺度上的影响。模型葡萄园土壤(马孔-法国)经历了一项长期的田间试验,其中包括使用各种材料和植物进行施肥和植被。我们特别研究了秸秆(S)和针叶树堆肥(CC)有机肥料以及三叶草(Cl)和羊茅(F)植被对这种壤土表层铜(杀菌剂)命运的影响,与未施肥土壤(NA)进行了比较。采集后,立即将这五种土壤进行物理分离,以获得 5 种粒级大小的土壤。对所有土壤和粒级大小进行了定量表征,包括颗粒组成、化学含量以及铜的分布、形态和对细菌和植物的生物利用度。结果表明,所有处理(Cl>CC>S>F>NA)的土壤成分聚集度都有明显增加,这与土壤成分与有机物(OM)的胶结程度增加有关。所有主要元素和有机碳的分布模式在土壤亚分级中变化很大,而且在 5 种处理之间也有很大差异。由于其特殊的无机和有机组成,土壤亚分级可以被认为是一个特定的微生物栖息地。添加的 OM 优先积累在 5 种土壤的 20-2 μm 和>250 μm 中。土壤亚分级中铜的分布模式及其形态和对细菌的生物利用度在 5 种土壤中差异很大,与 OM 的分布有关。我们的结果还表明,植物对铜的生物利用度受土壤-根际结构的控制。总的来说,我们的研究结果表明,葡萄园土壤的长期有机管理在宏观和微观尺度上都导致了土壤物理和化学性质的稳定变化。这些变化反过来又影响了铜的微观生物地球化学,特别是其对细菌和植物的生物利用度。