State Key Laboratory of Environmental Chemistry and Ecotoxicology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China; College of Resources and Environment, University of Chinese Academy of Sciences, Beijing 100049, China.
State Key Laboratory of Environmental Chemistry and Ecotoxicology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China; School of Environment, Hangzhou Institute for Advanced Study, UCAS, Hangzhou 310000, China.
Sci Total Environ. 2024 Aug 15;938:173385. doi: 10.1016/j.scitotenv.2024.173385. Epub 2024 May 24.
Internalization of chemicals and the forage risks of ryegrass under the combined exposure to PAHs and Cd at environmental concentrations were studied here. The effect of soil pH was also concerned due to the widely occurred soil acidification and general alkali remediation for acidification soil. Unexpectedly, as same as the acid-treated group (pH 6.77), the alkali-treatment (pH 8.83) increased Cd uptake compared with original soil pH group (pH 7.92) for the reason of CdOH and CdHCO formed in alkali-treated group. Co-exposure to PAHs induced more oxidative stress than Cd exposure alone due to PAHs aggregated in young root regions, such as root tips, and consequently, affecting the expression of Cd-transporters, destroying the basic structure of plant cells, inhibiting the energy supply for the transporters, even triggering programmed cell death, and finally resulting in decreased Cd uptake. Even under environmental concentrations, combined exposure caused potential risks derived from both PAHs and Cd. Especially, ryegrass grown in alkali-treated soil experienced an increased forage risks despite the soil meeting the national standards for Cd at safe levels. These comprehensive results reveal the mechanism of PAHs inhibiting Cd uptake, improve the understanding of bioavailability of Cd based on different forms, provide a theoretical basis to formulate the safety criteria, and guide the application of actual soil management.
本研究探讨了在环境浓度下多环芳烃(PAHs)和 Cd 联合暴露条件下,化学物质的内化和黑麦草的饲料风险。由于土壤酸化广泛发生以及普遍进行酸化土壤的碱修复,还关注了土壤 pH 值的影响。出乎意料的是,由于碱处理组(pH 8.83)中形成了 CdOH 和 CdHCO,与原始土壤 pH 值组(pH 7.92)相比,碱处理(pH 8.83)增加了 Cd 的吸收,就像酸处理组一样。由于 PAHs 聚集在年轻的根区,如根尖,导致比 Cd 单独暴露更严重的氧化应激,从而影响 Cd 转运蛋白的表达,破坏植物细胞的基本结构,抑制转运蛋白的能量供应,甚至引发程序性细胞死亡,最终导致 Cd 吸收减少。即使在环境浓度下,联合暴露也会带来源自 PAHs 和 Cd 的潜在风险。特别是,尽管土壤中 Cd 含量处于安全水平且符合国家标准,但在碱处理土壤中生长的黑麦草的饲料风险增加了。这些综合结果揭示了 PAHs 抑制 Cd 吸收的机制,提高了对基于不同形态的 Cd 生物利用度的认识,为制定安全标准提供了理论依据,并指导了实际土壤管理的应用。