State Key Laboratory of North China Crop Improvement and Regulation, College of Resources and Environmental Science, Hebei Agricultural University, Baoding, 071001, China.
State Key Laboratory of North China Crop Improvement and Regulation, College of Resources and Environmental Science, Hebei Agricultural University, Baoding, 071001, China.
Environ Pollut. 2023 Jun 15;327:121584. doi: 10.1016/j.envpol.2023.121584. Epub 2023 Apr 8.
Metal contamination is widespread, but only a few studies have evaluated the toxicological risks of metals (Cd, Cu, and Pb) in earthworms from farmlands in North China (Hebei province). Amynthas hupeiensis, the dominant species in the study area, was used to determine the responses and detoxification mechanisms of uncontaminated (CK), and low (LM)-, and high (HM)-metal-contaminated soils following 7-, 14-, and 28-days exposure. Metal toxicity in LM and HM soils inhibited the biomass of A. hupeiensis. The concentrations of Cd in A. hupeiensis bodies indicated accumulated Cd appeared to remain steady with prolonged exposure, while Cu/Pb increased significantly with soil levels. Bioaccumulation occurred in the order Cd > Pb > Cu in LM soil, and in the order Cd > Cu ≈ Pb in HM soil, which was attributed to differences in available fractions between LM and HM soils. Physiological levels of biomarkers in A. hupeiensis were determined, including total protein (TP), glutathione (GSH), glutathione peroxidase (GPx), acetylcholinesterase (AChE), and malondialdehyde (MDA). Deviations in GSH, GPx, and AChE were considered to denote sensitive biomarkers using the IBRv2 index. Metabolomics data (H nuclear magnetic resonance-based) revealed changes in metabolites following 28-days exposure to LM and HM soils. Differences in metabolism in A. hupeiensis following exposure to LM and HM were related to energy metabolism, amino acid biosynthesis, glycerophospholipid metabolism, inositol phosphate metabolism, and glutathione metabolism. Metal stress from LM and HM soils disturbed osmoregulation, resulting in oxidative stress, destruction of cell membranes and inflammation, and altered levels of amino acids required for energy by A. hupeiensis. These findings provide biochemical insights into the physiological and metabolic mechanisms underlying the ability of A. hupeiensis to resist metal stress, and for assessing the environmental risks of metal-contaminated soils in farmland in North China.
金属污染广泛存在,但仅有少数研究评估了华北地区(河北省)农田土壤中金属(Cd、Cu 和 Pb)的毒理学风险。研究区优势种宽水蚓(Amynthas hupeiensis)被用于确定未污染(CK)、低(LM)和高(HM)金属污染土壤在暴露 7、14 和 28 天后的响应和解毒机制。LM 和 HM 土壤中的金属毒性抑制了宽水蚓的生物量。宽水蚓体内 Cd 浓度表明,随着暴露时间的延长,积累的 Cd 似乎保持稳定,而 Cu/Pb 则随着土壤水平的升高而显著增加。在 LM 土壤中,生物累积顺序为 Cd > Pb > Cu,在 HM 土壤中,生物累积顺序为 Cd > Cu ≈ Pb,这归因于 LM 和 HM 土壤之间有效分数的差异。测定了宽水蚓体内的生理水平生物标志物,包括总蛋白(TP)、谷胱甘肽(GSH)、谷胱甘肽过氧化物酶(GPx)、乙酰胆碱酯酶(AChE)和丙二醛(MDA)。使用 IBRv2 指数,GSH、GPx 和 AChE 的偏差被认为是敏感的生物标志物。代谢组学数据(基于 H 核磁共振)显示,暴露于 LM 和 HM 土壤 28 天后代谢物发生变化。暴露于 LM 和 HM 土壤后宽水蚓代谢的差异与能量代谢、氨基酸生物合成、甘油磷脂代谢、肌醇磷酸盐代谢和谷胱甘肽代谢有关。LM 和 HM 土壤中的金属胁迫扰乱了渗透压调节,导致氧化应激、细胞膜破坏和炎症,以及宽水蚓用于能量的必需氨基酸水平发生变化。这些发现为宽水蚓抵抗金属胁迫的生理和代谢机制提供了生化见解,并为评估华北地区农田金属污染土壤的环境风险提供了依据。