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About the Journal
Superintended by:China North Industries Group Corporation Limited
Sponsoredy:Beijing Institute of Technology, Chinese Scoiety for Environmental Sciences, China Occupational Safety and Health Association
Edited & Published by: Editorial Department of Journal of Safety and Environment
Issues per year: 12
ISSN 1009-6094
CN 11-4537/X
Assessing the risks of mobilizing agents in the remediation of arsenic-contaminated soils: a case study of oxalic acid
CHEN Xiaochen;ZHANG Zengdi;WU Shiyu;LIU Xiaogang;YU Jianying;YAO Congcong;XU Jiayan;XU Huacheng;WEI Nan;In this study, we investigated the application risks of oxalic acid, a classic mobilizing agent, by examining arsenic(As) fractionation/speciation, leachability, and oral bioavailability/bioaccessibility. Advanced methodologies, including the toxicity characteristic leaching procedure and both in vivo and in vitro tests, were employed. The results revealed that oxalic acid significantly enhanced the mobility of arsenic in terms of fractionation. The proportion of labile arsenic(As) fractions, comprising the water-soluble and exchangeable fractions, increased by 1.85 times following mobilization. Concurrently, the combined proportion of amorphous and crystalline As was significantly reduced. This led to a marked increase in the ecological risk associated with soil As, with leachability rising by an average of 3.59 times. Notably, in both in vivo and in vitro tests, oxalic acid was found to reduce the health risks posed by arsenic. In the mouse model, oxalic acid significantly decreased the relative bioavailability of arsenic(As). Using the PBET-SHIME model, we observed that oxalic acid notably reduced As bioavailability during the colon phase. Additionally, oxalic acid inhibited the reduction of bioaccessible As(Ⅴ) and promoted the methylation of bioaccessible As(Ⅲ), which is associated with higher toxicity in colon fluid, thereby further mitigating health risks. The observed phenomena can primarily be attributed to the release of excessive metal components from the soil due to oxalic acid and the metabolism of oxalic acid by gut microbiota. Notably, consistent trends were observed across all soil samples following the application of oxalic acid, highlighting the generalizability of its effects on soil arsenic(As). In summary, as a typical low-molecular-weight organic acid, oxalic acid is highly recommended for the mobilization and remediation of As-contaminated soils. This study provides valuable scientific information for selecting mobilizing agents for As-contaminated soils and serves as a reference for risk control at remediation sites.
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Mechanistic insights into the enhanced synergistic removal of composite heavy metals using modified zeolite in constructed wetlands
DONG Shuangshi;ZHANG Shousen;JIANG Jingjing;ZHAO Zhenhao;XU Mingqian;SUN Di;JIN Xiaoyu;This study aims to develop an efficient and stable substrate material for artificial wetlands to treat copper-zinc composite heavy metal pollution in livestock wastewater. A nanoscale FeO/Fe2O_3-biochar-modified zeolite(FeC/Z-1:2) was synthesized using the co-precipitation method. The structural characteristics of the material were analyzed through SEM, XRD, FT-IR, and XPS. The preparation process involved mixing zeolite granules with biochar powder in a 1 mol/L solution, followed by 1 h of ultrasonication. The pH of the mixture is adjusted to approximately 7 using aqueous ammonia while stirring at 350 r/min. The slurry is then aged at room temperature for 24 hours before being dried at 60 ℃. Batch experiments were conducted to evaluate the effects of various carrier types, substrate ratios, and dosages on the removal of Cu and Zn. Results showed that zeolite particles outperformed other carriers in removing Cu and Zn, attributed to their smaller particle size and larger specific surface area. When the biochar-to-zeolite ratio was set at 1:2, the removal efficiencies for Cu2+ and Zn2+ at a concentration of 5 mg/L reached 94% and 100%, respectively. This performance was significantly superior to that achieved with nano-FeO/Fe2O3 or biochar alone. However, an excessive amount of biochar can hinder the exposure of active sites on nano-FeO/Fe2O3, leading to decreased removal rates. The optimal dosage of FeC/Z-1:2 for maximum Cu and Zn removal was determined to be 5 g. Mechanistic studies indicated that, firstly, the hydroxyl groups on the material's surface coordinate with metal ions to form metal hydroxide precipitates. Secondly, as the reaction progresses, Fe2+ is oxidized to Fe3+ and co-precipitates with heavy metal ions. These two processes synergistically contributed to the efficient removal of composite heavy metal pollution. Desorption experiments demonstrated that the material retains over 99.8% of heavy metals, indicating high environmental stability. This research offers new insights into the modification of artificial wetland substrates and presents a promising solution for addressing composite heavy metal pollution in livestock wastewater.
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Mechanisms of arsenic reduction and release from binary complex OM-As(Ⅴ) by arsenate-reducing bacteria
CAI Xiaolin;WU Min;LI Zejiao;WANG Pengfei;YIN Naiyi;CUI Yanshan;Soil arsenic(As) contamination represents a significant global environmental challenge. One of the predominant forms of As in soil is the formation of binary complexes between arsenate [As(Ⅴ)] and soil organic matter(OM), referred to as OM-As(Ⅴ). However, the mobilization and transformation processes of As within this binary complex, particularly in the presence of As(Ⅴ)-reducing bacteria, remain poorly understood. In this study, the binary complex OM-As(Ⅴ) was incubated with a typical As(Ⅴ)-reducing bacterial strain, Desulfitobacterium sp. DJ-3, under anoxic conditions for 144 h. During the incubation period, samples were collected destructively at various time points. The reduction and release of OM-complexed As during this incubation were systematically analyzed using liquid-phase chemical analysis and synchrotron radiation techniques. The results demonstrated that strain DJ-3 significantly enhanced the release of As by 25% and its reduction by 67% in the OM-As(Ⅴ) complex. Linear Combination Fitting(LCF) of the As K-edge XANES spectra indicated that strain DJ-3 could directly reduce OM-complexed As(Ⅴ) to complexed As(Ⅲ). After 144 hours, 50% of the As was found in the form of the binary complex OM-As(Ⅲ), resulting in the release of a portion of complexed As(Ⅲ) as free As(Ⅲ). This study utilized synchrotron radiation to demonstrate that As(Ⅴ)-reducing bacteria can not only reduce free As(Ⅴ) but also directly convert the binary complex OM-As(Ⅴ) to OM-As(Ⅲ). Furthermore, it was observed that some of the OM-complexed As(Ⅲ) is released as free As(Ⅲ) following this reduction process. This process not only increases the concentration of As(Ⅲ) in the soil environment but also raises the risk of As contamination in groundwater. Collectively, this study elucidates, for the first time, the mechanisms of As release and reduction in the binary complex OM-As(Ⅴ) mediated by As(Ⅴ)-reducing bacteria. The findings provide a scientific foundation for a comprehensive understanding of the mobilization and transformation of As in soil. Additionally, strain DJ-3 was found to effectively release As from binary organic matter complexes, suggesting its potential application in the leaching and remediation of As-contaminated soils with high organic matter content.
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Assessment of heavy metal pollution and source analysis in a typical ecological functional area of Chongqing City
YUE Rui;ZHANG Menglin;DUAN Jiahui;NING Mohuan;CHEN Xing;CHEN Guodong;This study aims to analyze the status and sources of heavy metal pollution in the ecological functional areas of Chongqing, focusing on Shizhu County as the study area. To effectively investigate the content and distribution characteristics of heavy metals, a total of 5 716 topsoil samples, 100 rock samples, and 5 slag samples were collected for analysis. The pollution status of heavy metals in the study area was evaluated using the Nemero composite pollution index, the single factor pollution index, and the land accumulation index. Furthermore, both correlation analysis and the Positive Matrix Factorization(PMF) model were employed to identify the sources of heavy metals. The results indicated that, based on the risk screening values, the excess rates for As, Cd, Cr, Cu, Hg, Ni, Pb, and Zn were 0.062 5%, 28.24%, 0.09%, 0.4%, 0.185%, 1.8%, 0.055%, and 0, respectively, highlighting significant variability among these metals. In terms of spatial distribution, areas with high concentrations of heavy metals are primarily located in the Permian and Triassic strata in the western and eastern parts of the study area, suggesting that heavy metal enrichment is closely related to the geological composition. The single factor index evaluation revealed that 31.24% of the area was classified as slightly polluted, indicating poor environmental quality for Cd in the study area. The Nemero composite pollution index indicated that the soil environment was predominantly clean(68.68%) or slightly polluted(28.49%). Additionally, the land accumulation index showed pollution rates of 23.31% for Cd, 11.24% for As, and 10.85% for Hg, suggesting that Cd is accumulating within the study area. The PMF source identification revealed three main sources of heavy metals in the study area: natural sources, agricultural and traffic mixed sources, and industrial sources, which accounted for 47.83%, 25.37%, and 26.78%, respectively. The concentration of Cd in the soil correlated with the Cd content in the underlying rocks. Additionally, the levels of heavy metals in the slag surrounding industrial and mining enterprises were significantly higher than the average values for the study area. This further indicates that the enrichment of heavy metals is closely related to both the natural background levels and industrial activities. The evaluation and source analysis of heavy metal pollution indicated that Cd contamination from natural and industrial sources is particularly prominent, posing a greater risk. These findings offer valuable scientific guidance for soil pollution control and the sustainable development and utilization of land resources in the study area.
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Study on a novel modified chitosan-based heavy metal chelating agent for treating Cu2+ in water and soil
XING Bo;YANG Qing;ZHANG Siyang;JIANG Caiyi;ZHANG Fuping;YANG Guo;LI Min;CHEN Tingting;FU Chaoting;This study presents a novel, cost-effective heavy metal chelator—dithiocarboxylate-functionalized polyaminoamide dendrimer(XCS-DTC)—synthesized from low-cost, readily available chitosan(CS) through a sequential modification process using chloroacetic acid(L) and carbon disulfide(CS2). Comprehensive characterization utilizing Fourier-transform infrared spectroscopy(FTIR), scanning electron microscopy(SEM), thermogravimetric analysis(TGA), and nitrogen adsorption-desorption isotherms confirmed the successful incorporation of abundant dithiocarboxyl functional groups(—S—CS-_2) and demonstrated exceptional thermal stability. The material exhibited exceptional efficacy in sequestering copper ions(Cu2+) from both aqueous systems and contaminated soils, with residual Cu2+ concentrations quantified using UV-spectrophotometry. Key findings include the optimization of synthesis parameters through systematic analysis of structure-performance relationships: a molar ratio of n(CS):n(L):n(NaOH):n(CS2) = 1:8:3:5, a reaction temperature of 30 ℃, a duration of 4 hours, and an operational pH range of 4-9. Under these conditions, XCS-DTC achieved a remarkable removal efficiency of 99.90% for aqueous Cu2+. Furthermore, XCS-DTC demonstrated superior chelation capacity compared to commercial agents such as Sodium Dimethyldithiocarbamate(SDD) and Na2S. It maintained a 99.90% removal rate of Cu2+ under acidic conditions(pH = 4) in aqueous treatments. At a dosage of 5%, it effectively immobilized 99.90% of Cu2+ across exchangeable, reducible, and oxidizable fractions in contaminated soil. The resulting XCS-DTC-Cu chelates exhibited remarkable environmental stability. Accelerated leaching tests revealed minimal metal release: only 0.24% Cu2+ leaching after 32 hours in a pH = 3 solution, and just 0.10% leaching from solidified soil after 24 hours of exposure at pH = 5. These values significantly align with China's GB 18598—2019 solid waste landfill standards. While XCS-DTC demonstrates exceptional promise for heavy metal remediation, its long-term environmental implications warrant further investigation. Challenges include trace metal leaching from chelates and economic feasibility, with an estimated operational cost of approximately 110 CNY/ton for treating organic heavy metal wastewater. Future research should focus on conducting comprehensive lifecycle assessments that encompass production, deployment, and disposal phases, as well as developing cost-optimized synthesis protocols to facilitate industrial adoption.
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