Huang Yiting, Tang Yankui, Xie Zhenze, Wu Jipeng, Huang Jiajie, Nie Shaojiang
School of Civil Engineering and Architecture, Guangxi University, Nanning 530004, China.
School of Resources, Environment, and Materials, Guangxi University, Nanning 530004, China.
Toxics. 2025 Jun 13;13(6):496. doi: 10.3390/toxics13060496.
The influence of petroleum hydrocarbons (PHCs) on the transport and transformation of heavy metals may limit bioremediation efficiency. The mechanisms by which PHC degradation intermediates control heavy metal distribution in calcareous soils from karst areas require further exploration. This study systematically investigated how compositional changes in diesel fuel during aging regulated the fate of Cd and Pb in calcareous soils. The results demonstrated that the low-molecular-weight fractions of diesel fuel (C-C) were preferentially degraded. This degradation process altered zeta potential, cation exchange capacity (CEC), and pH, thereby promoting Cd stabilization through electrostatic attraction and speciation transformation. Particularly, reducible Cd content showed a strong positive correlation with C content ( = 0.88, < 0.05). Furthermore, the degradation of C-C fractions caused Pb transformation from residual to bioavailable fractions by stimulating microbial activity. Residual Pb content was positively correlated with C-C fractions ( = 0.55, < 0.05). Notably, dissolved organic matter (DOM) and CaCO content in calcareous soils enhanced Cd and Pb adsorption, thereby weakening the interactions between these metals and C-C fractions. Consequently, multiple linear regression (MLR) models relying exclusively on C-C degradation parameters showed poor fitting coefficients for Cd/Pb mobility. The present work provides scientific guidance for heavy metal bioremediation in calcareous soils.
石油烃(PHCs)对重金属迁移转化的影响可能会限制生物修复效率。PHC降解中间体控制喀斯特地区石灰性土壤中重金属分布的机制尚需进一步探索。本研究系统地研究了老化过程中柴油成分的变化如何调节石灰性土壤中Cd和Pb的归宿。结果表明,柴油的低分子量组分(C-C)优先降解。这一降解过程改变了zeta电位、阳离子交换容量(CEC)和pH值,从而通过静电吸引和形态转化促进了Cd的稳定。特别是,可还原态Cd含量与C含量呈强正相关(r = 0.88,P < 0.05)。此外,C-C组分的降解通过刺激微生物活性导致Pb从残留态向生物可利用态转化。残留态Pb含量与C-C组分呈正相关(r = 0.55,P < 0.05)。值得注意的是,石灰性土壤中的溶解有机物(DOM)和CaCO₃含量增强了对Cd和Pb的吸附,从而削弱了这些金属与C-C组分之间的相互作用。因此,仅依赖C-C降解参数的多元线性回归(MLR)模型对Cd/Pb迁移性的拟合系数较差。本研究为石灰性土壤中重金属生物修复提供了科学指导。