{"title":"Effects of citric acid on Cd speciation in biochar-amended contaminated soils.","authors":"Bingyao Xu, Jiayu Xu, Meiqi Wang, Weifeng Chen, Usman Farooq, Renhui Miao, Zhichong Qi","doi":"10.1007/s10653-025-02596-5","DOIUrl":null,"url":null,"abstract":"<p><p>Understanding the roles of low-molecular-weight organic acids (LMWOAs) in the transformation of chemical speciation of heavy metals in contaminated soil amended by biochar is of great significance for assessing the effectiveness of this carbonaceous amendment. The impacts of citric acid (a typical LMWOA) on the redistribution of Cd in contaminated soil amended by different amounts of biochar (1-5%) generated at various pyrolysis temperatures (300 ~ 700 °C) were investigated in this study. Biochar treatments reduced the exchangeable fraction (F1) of Cd after one year of incubation. Meanwhile, biochars produced at lower temperatures with more surface functional groups showed better immobilization performances (e.g., the F1 values decreased from 54.5% (CK) to 31.7% (adding 5% biochar generated at 300 °C) and 37.3% (adding 5% biochar generated at 700 °C), respectively). In comparison, the iron and manganese-bound fraction (F3) and organic bound fraction (F4) of Cd exhibited increased trends because of the increase in Cd linked to organic compounds and mineral oxides of soil particles. The residual fraction (F5) also showed an increased trend within a long remediation action. That is, the application of biochars favored the Cd redistribution into more stable speciations and led to a decrease in mobility. However, the addition of citric acid was beneficial in transforming immobilized fractions of Cd into mobilized fractions due to the H<sup>+</sup>-driven dissolution and release of Cd precipitation (e.g., for the soil treated with 3% biochar generated at 300 °C, the F1 values increased from 35.9% (before adding citric acid) to 43.5% (after adding citric acid)). Moreover, the high ratio of biochar addition could buffer soil pH reduction caused by adding citric acid and inhibit the dissolution of Cd. The findings have implications for assessing the effectiveness of biochar used as an amendment for reducing the risk of Cd in the rhizosphere of contaminated soils.</p>","PeriodicalId":11759,"journal":{"name":"Environmental Geochemistry and Health","volume":"47 7","pages":"278"},"PeriodicalIF":3.2000,"publicationDate":"2025-06-21","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Environmental Geochemistry and Health","FirstCategoryId":"93","ListUrlMain":"https://doi.org/10.1007/s10653-025-02596-5","RegionNum":3,"RegionCategory":"环境科学与生态学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q3","JCRName":"ENGINEERING, ENVIRONMENTAL","Score":null,"Total":0}
引用次数: 0
Abstract
Understanding the roles of low-molecular-weight organic acids (LMWOAs) in the transformation of chemical speciation of heavy metals in contaminated soil amended by biochar is of great significance for assessing the effectiveness of this carbonaceous amendment. The impacts of citric acid (a typical LMWOA) on the redistribution of Cd in contaminated soil amended by different amounts of biochar (1-5%) generated at various pyrolysis temperatures (300 ~ 700 °C) were investigated in this study. Biochar treatments reduced the exchangeable fraction (F1) of Cd after one year of incubation. Meanwhile, biochars produced at lower temperatures with more surface functional groups showed better immobilization performances (e.g., the F1 values decreased from 54.5% (CK) to 31.7% (adding 5% biochar generated at 300 °C) and 37.3% (adding 5% biochar generated at 700 °C), respectively). In comparison, the iron and manganese-bound fraction (F3) and organic bound fraction (F4) of Cd exhibited increased trends because of the increase in Cd linked to organic compounds and mineral oxides of soil particles. The residual fraction (F5) also showed an increased trend within a long remediation action. That is, the application of biochars favored the Cd redistribution into more stable speciations and led to a decrease in mobility. However, the addition of citric acid was beneficial in transforming immobilized fractions of Cd into mobilized fractions due to the H+-driven dissolution and release of Cd precipitation (e.g., for the soil treated with 3% biochar generated at 300 °C, the F1 values increased from 35.9% (before adding citric acid) to 43.5% (after adding citric acid)). Moreover, the high ratio of biochar addition could buffer soil pH reduction caused by adding citric acid and inhibit the dissolution of Cd. The findings have implications for assessing the effectiveness of biochar used as an amendment for reducing the risk of Cd in the rhizosphere of contaminated soils.
期刊介绍:
Environmental Geochemistry and Health publishes original research papers and review papers across the broad field of environmental geochemistry. Environmental geochemistry and health establishes and explains links between the natural or disturbed chemical composition of the earth’s surface and the health of plants, animals and people.
Beneficial elements regulate or promote enzymatic and hormonal activity whereas other elements may be toxic. Bedrock geochemistry controls the composition of soil and hence that of water and vegetation. Environmental issues, such as pollution, arising from the extraction and use of mineral resources, are discussed. The effects of contaminants introduced into the earth’s geochemical systems are examined. Geochemical surveys of soil, water and plants show how major and trace elements are distributed geographically. Associated epidemiological studies reveal the possibility of causal links between the natural or disturbed geochemical environment and disease. Experimental research illuminates the nature or consequences of natural or disturbed geochemical processes.
The journal particularly welcomes novel research linking environmental geochemistry and health issues on such topics as: heavy metals (including mercury), persistent organic pollutants (POPs), and mixed chemicals emitted through human activities, such as uncontrolled recycling of electronic-waste; waste recycling; surface-atmospheric interaction processes (natural and anthropogenic emissions, vertical transport, deposition, and physical-chemical interaction) of gases and aerosols; phytoremediation/restoration of contaminated sites; food contamination and safety; environmental effects of medicines; effects and toxicity of mixed pollutants; speciation of heavy metals/metalloids; effects of mining; disturbed geochemistry from human behavior, natural or man-made hazards; particle and nanoparticle toxicology; risk and the vulnerability of populations, etc.