ISPA, Bordeaux Sciences Agro, INRAE, 33140, Villenave d'Ornon, France.
Université de Pau et des Pays de l'Adour, e2s UPPA, CNRS, IPREM-UMR, 5254, Hélioparc, Pau, France.
Environ Pollut. 2024 Sep 1;356:124382. doi: 10.1016/j.envpol.2024.124382. Epub 2024 Jun 17.
Aerated compost teas (ACTs) are rich in soluble humic substances (SHS) that have high affinity for metals, notably Cu. Using a batch experiment, we measured the extent to which two ACTs altered Cu dynamics in vineyard topsoils one day and 21 days after their addition. Soils were extracted with 0.01 M KCl, and total Cu concentration, free Cu ion fraction and size distribution of Cu ligands were measured in the extraction solution to assess the impact of ACT on the mobility of Cu. Diffusive gradient in thin film (DGT) measurements were carried out to assess the effect of ACT on Cu bioavailability, and the dissociation rate of Cu-SHS complexes was measured. The results revealed that ACT increased the mobility of Cu from a factor 1.2 to 5.8 depending on the soil, the ACT and the incubation time. Cu mobilization was associated with an increase in absorbance at 254 nm and a decrease in the free Cu ion fraction in the KCl extract. Associated with the strong agreement between the size distribution of SHS and that of Cu ligands in the KCl extract of soils treated with ACT, these results showed that Cu was mobilized through complexation by the SHS present in ACTs. A fraction of the SHS supplied with ACTs sorbed onto the soil constituents, notably in calcareous soils where this fraction reached 86% for ACT B. Between 15% and 50% of the SHS remaining in solution degraded between day one and day 21 under the presumed action of microflora. This explains why the Cu mobilization efficiency of ACTs was on average lower in calcareous soils than in non-calcareous soils, and decreased with time. Lastly, ACT increased the bioavailability of Cu in soils from a factor 1.3 to 4.2, due to the relatively high dissociation rate of Cu-SHS complexes.
充气堆肥茶(ACTs)富含具有高金属亲和力的可溶性腐殖质(SHS),尤其是 Cu。采用批量实验,我们测量了两种 ACT 在添加后一天和 21 天后对葡萄园表土中 Cu 动态的影响程度。使用 0.01 M KCl 提取土壤,测量提取液中总 Cu 浓度、游离 Cu 离子分数和 Cu 配体的大小分布,以评估 ACT 对 Cu 迁移性的影响。进行扩散梯度薄膜(DGT)测量以评估 ACT 对 Cu 生物有效性的影响,并测量 Cu-SHS 配合物的离解速率。结果表明,ACT 增加了 Cu 的迁移性,其程度取决于土壤、ACT 和培养时间,从 1.2 倍到 5.8 倍不等。Cu 的迁移与 254nm 处吸光度的增加和 KCl 提取物中游离 Cu 离子分数的降低有关。与 ACT 处理土壤中 KCl 提取物中 SHS 大小分布与 Cu 配体大小分布之间的强烈一致性有关,这些结果表明,Cu 通过 ACT 中存在的 SHS 络合而被迁移。一部分 ACT 提供的 SHS 吸附在土壤成分上,特别是在钙质土壤中,这种成分达到 ACT B 的 86%。在假定微生物作用下,在第 1 天到第 21 天之间,留在溶液中的 SHS 有 15%到 50%发生降解。这解释了为什么 ACT 对钙质土壤中 Cu 的迁移效率平均低于非钙质土壤,并且随着时间的推移而降低。最后,ACT 通过提高 Cu-SHS 配合物的相对高离解速率,将土壤中 Cu 的生物有效性提高了 1.3 到 4.2 倍。