College of Environmental Science and Engineering, Central South University of Forestry and Technology, Changsha 410004, China; Hunan Engineering Laboratory for Control of Rice Quality and Safety, Changsha 410004, China.
College of Environmental Science and Engineering, Central South University of Forestry and Technology, Changsha 410004, China; Hunan Engineering Laboratory for Control of Rice Quality and Safety, Changsha 410004, China.
Sci Total Environ. 2022 Jul 15;830:154633. doi: 10.1016/j.scitotenv.2022.154633. Epub 2022 Mar 18.
The practical application of in situ remediation techniques requires an understanding of the dynamic changes in soil enzyme activity as indicators of soil fertility and health. Experiments were carried out in paddy soils co-contaminated with cadmium (Cd) and arsenic (As) at low (L) and high (H) levels. A calcium and iron (CaFe)-based amendment (limestone + iron powder + silicon fertilizer + calcium‑magnesium-phosphate fertilizer) was applied to the soil at concentrations of 0, 450, and 900 g·m (labeled CK, T1, and T2, respectively), and sampling was conducted at the tillering (TS), booting (BS), filling (FS), and mature (MS) stages. In soil L, urease activity increased significantly by 15.8% under T1 treatment at the MS, catalase activity increased significantly under T2 treatment by 52.4% at the FS and 25.9% at the MS, and acid phosphatase activity increased significantly by 50.1%-65.9% at the TS. For soil H, urease activity increased by maximum values of 101.6% and 28.6% at the FS and MS, respectively. Catalase activity increased by 29.0% at the MS under T2 treatment, and acid phosphatase activity increased by maximum values of 40.5%, 16.0%, and 53.9% at the BS, FS, and MS, respectively. The results indicate that the changes in soil enzyme activity were mainly related to the rice growth stage, soil pH, and available Cd and As after the application of Ca-Fe-based amendment. Overall, at the FS and MS, the amendment increased the soil pH, soil enzyme activity, and cation exchange capacity and reduced the available Cd and As, which reduced the Cd and As contents in brown rice.
原位修复技术的实际应用需要了解土壤酶活性的动态变化,将其作为土壤肥力和健康的指标。本实验在镉(Cd)和砷(As)低(L)、高(H)水平共污染的稻田土壤中进行。在土壤中施加钙铁(CaFe)基改良剂(石灰+铁粉+硅肥+钙镁磷肥),浓度分别为 0、450 和 900 g·m(分别标记为 CK、T1 和 T2),并在分蘖(TS)、孕穗(BS)、灌浆(FS)和成熟(MS)阶段进行采样。在土壤 L 中,T1 处理下 MS 时脲酶活性显著增加 15.8%,T2 处理下 FS 时过氧化氢酶活性显著增加 52.4%,MS 时增加 25.9%,T1 处理下 TS 时酸性磷酸酶活性显著增加 50.1%-65.9%。对于土壤 H,FS 和 MS 时脲酶活性分别达到最大增加 101.6%和 28.6%。T2 处理下 MS 时过氧化氢酶活性增加 29.0%,T1 处理下 BS、FS 和 MS 时酸性磷酸酶活性分别达到最大增加 40.5%、16.0%和 53.9%。结果表明,土壤酶活性的变化主要与水稻生长阶段、土壤 pH 值以及施用 CaFe 基改良剂后土壤中有效态 Cd 和 As 有关。总体而言,在 FS 和 MS 时,改良剂增加了土壤 pH 值、土壤酶活性和阳离子交换容量,降低了有效态 Cd 和 As,从而降低了糙米中 Cd 和 As 的含量。