Degradation of Low-Molecular-Weight Diesel Fractions (C10-C16 Alkane) Drives Cd Stabilization and Pb Activation in Calcareous Soils from Karst Areas.

IF 4.1 3区 环境科学与生态学 Q2 ENVIRONMENTAL SCIENCES
Toxics Pub Date : 2025-06-13 DOI:10.3390/toxics13060496
Yiting Huang, Yankui Tang, Zhenze Xie, Jipeng Wu, Jiajie Huang, Shaojiang Nie
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引用次数: 0

Abstract

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 (C10-C16) 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 C16 content (r = 0.88, p < 0.05). Furthermore, the degradation of C10-C16 fractions caused Pb transformation from residual to bioavailable fractions by stimulating microbial activity. Residual Pb content was positively correlated with C10-C16 fractions (r = 0.55, p < 0.05). Notably, dissolved organic matter (DOM) and CaCO3 content in calcareous soils enhanced Cd and Pb adsorption, thereby weakening the interactions between these metals and C10-C16 fractions. Consequently, multiple linear regression (MLR) models relying exclusively on C10-C16 degradation parameters showed poor fitting coefficients for Cd/Pb mobility. The present work provides scientific guidance for heavy metal bioremediation in calcareous soils.

低分子柴油馏分(C10-C16烷烃)降解对喀斯特地区钙质土壤Cd稳定和Pb活化的影响
石油烃(PHCs)对重金属运输和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钙质土壤中重金属分布的机制有待进一步探讨。本研究系统地研究了老化过程中柴油成分变化对钙质土壤中镉和铅的影响。结果表明,柴油低分子量组分(C10-C16)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镉的稳定。还原性Cd含量与C16含量呈显著正相关(r = 0.88, p < 0.05)。此外,C10-C16组分的降解通过刺激微生物活性使铅从残留组分转化为生物可利用组分。残余Pb含量与c10 ~ c16组分呈正相关(r = 0.55, p < 0.05)。钙质土壤中溶解有机物(DOM)和CaCO3的含量增强了Cd和Pb的吸附,从而减弱了这些金属与C10-C16组分之间的相互作用。因此,仅依赖C10-C16降解参数的多元线性回归(MLR)模型对Cd/Pb迁移率的拟合系数较差。本研究为钙质土壤重金属的生物修复提供了科学指导。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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来源期刊
Toxics
Toxics Chemical Engineering-Chemical Health and Safety
CiteScore
4.50
自引率
10.90%
发文量
681
审稿时长
6 weeks
期刊介绍: Toxics (ISSN 2305-6304) is an international, peer-reviewed, open access journal which provides an advanced forum for studies related to all aspects of toxic chemicals and materials. It publishes reviews, regular research papers, and short communications. Our aim is to encourage scientists to publish their experimental and theoretical results in detail. There is, therefore, no restriction on the maximum length of the papers, although authors should write their papers in a clear and concise way. The full experimental details must be provided so that the results can be reproduced. Electronic files or software regarding the full details of calculations and experimental procedure can be deposited as supplementary material, if it is not possible to publish them along with the text.
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