College of Resources and Environmental Science, Yunnan Agricultural University, Kunming 650201, China; State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.
State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.
Environ Pollut. 2024 Apr 1;346:123704. doi: 10.1016/j.envpol.2024.123704. Epub 2024 Mar 3.
East Yunnan province in southwest China is a region with elevated natural abundance (high geological background levels) of Cd due to high metal (loid) contents in the soils. Enzyme activities are useful indicators of metal (loid) toxicity in contaminated soils and whether Cd inhibits enzyme activities in paddy soils in high geological background areas is of considerable public concern. A pot experiment combined with field investigation was conducted to assess the effects of Cd on six soil enzymes that are essential to the cycling of C, N, and P in soils. Inhibitory effects of Cd fractions on enzyme activities were assessed using ecological dose-response models. The impact of soil properties on the inhibition of sensitive soil enzymes by Cd were assessed using linear and structural equation models. Cadmium was enriched in the paddy soils with 72.2 % of soil samples from high geological background areas exceeding the Chinese threshold values (GB 15618-2018) of Cd. Enzyme responses to Cd contamination varied markedly with a negative response by catalase but a positive response by invertase. Urease, β-glucosidase, and alkaline phosphatase activities were stimulated at low Cd concentrations and inhibited at high concentrations. The average inhibition ratios of β-glucosidase, urease, and catalase in high Cd levels were 19.9, 38.9, and 51.9%, respectively. Ecological dose-response models indicate that catalase and urease were the most Cd-sensitive of the enzymes studied and were suitable indicators of soil quality in high geological background areas. Structural equation modeling (SEM) indicates that soil properties influenced sensitive enzymes through various pathways, indicating that soil properties were factors determining Cd inhibition of enzyme activities. This suggests that Cd concentrations and soil physicochemical properties under a range of environmental conditions should be considered in addressing soil Cd pollution.
中国西南部的滇东地区由于土壤中金属(类)含量高,导致其自然丰度(高地质背景水平)升高。酶活性是污染土壤中金属(类)毒性的有用指标,而 Cd 是否抑制高地质背景地区稻田土壤中的酶活性则引起了相当大的公众关注。采用盆栽试验与田间调查相结合的方法,评估了 Cd 对土壤中与 C、N 和 P 循环有关的 6 种土壤酶的影响。采用生态剂量反应模型评估 Cd 各形态对酶活性的抑制作用。采用线性和结构方程模型评估土壤性质对 Cd 抑制敏感土壤酶的影响。结果表明:高地质背景地区的稻田土壤中 Cd 富集,72.2%的土壤样本超过中国土壤 Cd 标准值(GB 15618-2018)。土壤酶对 Cd 污染的响应差异显著,过氧化氢酶呈负响应,而转化酶呈正响应。脲酶、β-葡萄糖苷酶和碱性磷酸酶在低 Cd 浓度下受到刺激,在高浓度下受到抑制。高 Cd 水平下,β-葡萄糖苷酶、脲酶和过氧化氢酶的平均抑制率分别为 19.9%、38.9%和 51.9%。生态剂量反应模型表明,过氧化氢酶和脲酶是研究的酶中最敏感的酶,是高地质背景地区土壤质量的适宜指标。结构方程模型(SEM)表明,土壤性质通过多种途径影响敏感酶,表明土壤性质是决定酶活性受 Cd 抑制的因素。这表明在解决土壤 Cd 污染时,应考虑 Cd 浓度和不同环境条件下的土壤物理化学性质。