School of Environmental Science and Engineering, Shandong University, China-America CRC for Environment & Health, Shandong Province, 72# Jimo Binhai Road, Qingdao, Shandong, 266237, People's Republic of China.
Yanzhou District Branch of Jining Ecological Environment Bureau, No. 159, Wenhua East Road , Yanzhou District, Jining City, Shandong Province, 272100, People's Republic of China.
Environ Sci Pollut Res Int. 2022 Jun;29(26):40012-40028. doi: 10.1007/s11356-022-18990-w. Epub 2022 Feb 3.
Phenanthrene (PHE) contamination not only changes the quality of soil environment but also threatens to the soil organisms. There is lack of focus on the eco-toxicity potential of this contaminant in real soil in the current investigation. Here, we assessed the toxic effects of PHE on earthworms (Eisenia fetida) in natural soil matrix. PHE exhibited a relatively high toxicity to E. fetida in natural soil, with the LC determined to be 56.68 mg kg after a 14-day exposure. Excessive ROS induced by PHE, leading to oxidative damage to biomacromolecules in E. fetida, including lipid peroxidation, protein carbonylation, and DNA damage. The antioxidant defense system (total antioxidant capacity, glutathione S-transferase, peroxidase, catalase, carboxylesterase, and superoxide dismutase) in E. fetida responded quickly to scavenge excess ROS and free radicals. Exposure to PHE resulted in earthworm avoidance responses (2.5 mg kg) and habitat function loss (10 mg kg). Histological observations indicated that the intestine, body wall, and seminal vesicle in E. fetida were severely damaged after exposure to high-dose PHE. Moreover, earthworm growth (weight change) and reproduction (cocoon production and the number of juvenile) were also inhibited after exposure to this pollutant. Furthermore, the integrated toxicity of PHE toward E. fetida at different doses and exposure times was assessed by the integrated biomarker response (IBR), which confirmed that PHE is more toxic to earthworms in the high-dose and long-term exposure groups. Our results showed that PHE exposure induced oxidative stress, disturbed antioxidant defense system, and caused oxidative damage in E. fetida. These effects can trigger behavior changes and damage histological structure, finally cause growth inhibition, genotoxicity, and reproductive toxicity in earthworms. The strength of this study is the comprehensive toxicity evaluation of PHE to earthworms and highlights the need to investigate the eco-toxicity potential of exogenous environmental pollutants in a real soil environment.
菲(PHE)污染不仅改变了土壤环境的质量,还威胁到土壤生物。在当前的研究中,人们缺乏对这种污染物在实际土壤中生态毒性潜力的关注。在这里,我们评估了 PHE 在自然土壤基质中对蚯蚓(赤子爱胜蚓)的毒性作用。PHE 在自然土壤中对 E. fetida 表现出相对较高的毒性,在 14 天暴露后,LC 确定为 56.68 mg kg。PHE 诱导过多的 ROS,导致 E. fetida 生物大分子发生氧化损伤,包括脂质过氧化、蛋白质羰基化和 DNA 损伤。E. fetida 中的抗氧化防御系统(总抗氧化能力、谷胱甘肽 S-转移酶、过氧化物酶、过氧化氢酶、羧酸酯酶和超氧化物歧化酶)迅速响应,清除过多的 ROS 和自由基。暴露于 PHE 会导致蚯蚓回避反应(2.5 mg kg)和栖息地功能丧失(10 mg kg)。组织学观察表明,E. fetida 的肠道、体壁和精囊在暴露于高剂量 PHE 后受到严重损伤。此外,暴露于这种污染物后,蚯蚓的生长(体重变化)和繁殖(茧的产生和幼体数量)也受到抑制。此外,通过整合生物标志物响应(IBR)评估了不同剂量和暴露时间下 PHE 对 E. fetida 的综合毒性,这证实了 PHE 在高剂量和长期暴露组对蚯蚓的毒性更大。我们的研究结果表明,PHE 暴露会引起氧化应激,扰乱抗氧化防御系统,并导致 E. fetida 发生氧化损伤。这些影响会引发行为变化和破坏组织学结构,最终导致蚯蚓生长抑制、遗传毒性和生殖毒性。本研究的优势在于全面评估了 PHE 对蚯蚓的综合毒性,并强调了需要在实际土壤环境中调查外源性环境污染物的生态毒性潜力。