Optimization of Operating Parameters for the Selective Flotation of Heavy Metals from Contaminated Fine Sediment Using Response Surface Model

In this study, the effect of different flotation operating variables, such as pH, pulp density, collector concentration, impeller speed, frother concentration, and air flow rate, on selective flotation of heavy metals, especially Cu, from fine dredged sediment has been evaluated. Parameter optimization was done using the single parameter at a time method and response surface method (RSM) using Box-Behnken design and was assessed in terms of metal removal, metal recovery, metal concentration factor, and mass recovery. Among the operating variables studied, pulp pH, collector concentration, pulp density, and impeller speed were found to have significant effect on metal flotation selectivity. A validation study of the response surface model showed its aptness to predict the optimum values of operating parameters and their interactions on flotation responses which evaluate flotation performance. Flotation experiments under optimum operating parameters showed good flotation selectivity for Cu (3.3 ± 0.2) with a mass recovery of (mass of sediment in the froth) 14.1 ± 1 and Cu removal of 37.4 ± 3.6%.     

Removal of Heavy Metals from Contaminated Soil and Sediments Using the Biosurfactant Surfactin

The feasibility of using a biodegradable surfactant, surfactin from Bacillus subtilis, for the removal of heavy metals from a contaminated soil (890?mg/kg zinc, 420?mg/kg copper, 12.6% oil and grease) and sediments (110?mg/kg copper, 3300?mg/kg zinc) was evaluated. Results showed that after one and five batch washings of the soil, 25 and 70% of the copper, 6 and 25% of the zinc, and 5 and 15% of the cadmium could be removed by 0.1% surfactin with 1% NaOH, respectively. From the sediment, 15% of the copper and 6% of the zinc could be removed after a single washing with 0.25% surfactin/1% NaOH. The geochemical speciation of the heavy metals among the exchangeable, oxide, carbonate, organic, and residual fractions was determined by selective sequential extraction procedure. For both matrices, the exchangeable fractions were minimal, while the carbonate and the oxide fractions accounted for over 90% of the zinc present and the organic fraction constituted over 70% of the copper. Results after washing indicated that surfactin with NaOH could remove copper from the organic fraction, zinc from the oxide, and cadmium from the carbonate fractions. The residual fraction remained untouched. These experiments indicate that the sequential extraction studies could be useful in designing soil-washing procedures.     

HCl-Extractable Metal Profiles Correlate with Bacterial Population Shifts in Metal-Impacted Anoxic Coastal Sediment from the Wet/Dry Tropics

Metal impacted, anoxic sediments from five sites at a coastal location in the wet/dry tropics of Australia were sampled during both wet and dry seasons. Metal concentrations in total sediment and porewater, and in potentially bioavailable and bioaccessible fractions, were measured. Pyrosequencing was used to sequence bacterial DNA extracted from the sediment, and the sequence data was used to generate community profiles at each sample site. Changes in bacterial populations between sites reflected changes in the concentrations of 7 metals/metalloids (Al, V, Mo, Ga, Zn, Cd, As), and best correlated with the HCl-extractable fraction of metals. Bacterial community structure was also related to physicochemical factors, such as redox potential and organic carbon. Despite a strong sulphide gradient across the transect, acid-volatile sulphide was not significantly correlated to bacterial community structure. We conclude that the bioaccessible fraction of metals to bacteria is partly comprised of particulates, and porewater alone is not a sufficient model for potential metal impact.

[Supplementary materials are available for this article. Go to the publisher's online edition of Geomicrobiology Journal to view the two supplementary tables.]     

Using Contaminated Plants Involved in Phytoremediation for Anaerobic Digestion

This study investigated the anaerobic digestion capability of five plants and the effects of copper (Cu) and S,S’-ethylenediaminedisuccinic acid (EDDS, a chelator widely used in chelant-assisted phytoremediation) on biogas production to determine a feasible disposal method for plants used in remediation. The results showed that in addition to Phytolacca americana L., plants such as Zea mays L., Brassica napus L., Elsholtzia splendens Nakai ex F. Maekawa, and Oenothera biennis L. performed well in biogas production. Among these, O. biennis required the shortest period to finish anaerobic digestion. Compared to normal plants with low Cu content, the plants used in remediation with increased Cu levels (100 mg kg^?1) not only promoted anaerobic digestion and required a shorter anaerobic digestion time, but also increased the methane content in biogas. When the Cu content in plants increased to 500, 1000, and 5000 mg kg^?1, the cumulative biogas production decreased by 12.3%, 14.6%, and 41.2%, respectively. Studies also found that EDDS conspicuously restrained biogas production from anaerobic digestion. The results suggest that anaerobic digestion has great potential for the disposal of contaminated plants and may provide a solution for the resource utilization of plants used in remediation.     

Migration and Stabilization of Multiple Heavy Metals in an Aged Contaminated Soil under a Constant Voltage Electric Field

With the aim of metal decontamination, migration and stabilization of multiply heavy metals in an aged contaminated soil under a constant 1 V cm^?1 parallel-plate electric field were investigated through monitoring the metal migration in the anolyte, as well as analyzing their species distribution residual in soil. Besides anionic Cr(VI), cationic metals were also found in the anolyte, primarily by the concentration-gradient-driven diffusion of free ions, especially when the produced H⁺ considerably increased their levels in the soil. After 295 h, parts of Cu, Cr, Ni, and Zn were found to electro-migrate into the intermediate area, but no obvious Pb migration was observed, likely ascribed to its own great inertia and precipitation with the present Cr(VI). However, in the whole, only 5.3% of Zn and 2.7% of Ni were separated, while the release of other heavy metals was almost ignorable. Although Pb mobility in the soil near the anode even increased three times, the overall metal mobility in all sample locations was found to significantly reduce under the electric field, indicating an effective stabilization approach. Moreover, compared with the bottom soil, the top soil near the anode was found to have a lower pH, higher moisture, lower heavy metal concentrations, and less soil oxidant demand; these phenomena may be due to a faster electro-migration of charged ions, especially H⁺, in the top soil. Therefore, such a divergence may considered to improve the current simulation approach for a realistic estimation of the actual metal and H⁺ electro-migration rate and the associated behavior under an electric field.     

固体介质中的重金属源解析及其在中国近海沉积物中的应用

沉积物中重金属源解析对甄别人为活动与自然变化对近海生态系统演化的影响有重要作用.本文总结了近年来污染物源解析常用的多元统计分析、地球化学方法和地质统计分析3种主要研究方法,剖析了不同方法的优劣及适用性,提出正定矩阵因子分析、Pb同位素示踪在重金属来源定量化研究中具有良好应用前景.梳理了中国近海沉积物中重金属来源的主要研究结果,发现河口和海湾是沉积物重金属受人为来源影响剧烈的典型近海区域,不同定量解析方法(多元统计分析、背景值估算、Pb同位素分析)均表明中国近海沉积物重金属的人为来源贡献率接近或超过50%.当前中国近海沉积物中重金属源解析研究还存在源识别端元模糊、解析结果缺乏相应的可靠性评价等问题.据此提出近海沉积物重金属源解析研究应使用多种解析技术手段综合、集成与优化,提高源解析的准确性;建立完善指标体系,筛选代表特定人为活动和自然过程的指标;甄别人为源重金属入海方式及过程,为沉积物数据信息的解译提供理论基础.     

Simultaneous Treatment of Dioxins and Heavy Metals in Tagonoura Harbor Sediment by Two-Step Pyrolysis

This paper describes the simultaneous treatment of PCDD/PCDF and toxic heavy metals contaminated sediment by pyrolysis with emphasis on complete removal and destruction of PCDD/PCDF in Tagonoura harbor sediment during a two-step pyrolysis process. Pyrolysis was conducted at different temperatures and N ₂ gas flow rates. Results showed that almost all PCDD/PCDF (99.998%) can be removed from the sediment by treatment at 800°C for 30 minutes in single-step pyrolysis; however, PCDD/PCDF remained in the gas phase without destruction. Analysis also revealed that some PCDD/PCDF formation occurred during the single-step pyrolysis. However, by the use of two-step pyrolysis, where off-gases from the first furnace are heated at 1000°C, PCDD/PCDF in the final gas effluent was dramatically reduced by a thermal degradation mechanism. Stabilization of toxic heavy metals was also observed. Specifically, their leaching activity drastically decreased with increasing pyrolysis temperature. Significant metal volatilization did not occur. Though the low temperature pyrolysis was effective in removing PCDD/PCDF, the leachability of toxic heavy metals such as Cr and Ni was higher that of 800°C; however, lower than untreated. Two-step pyrolysis at 800°C for 30 minutes in the single-step and 1000°C in the two-step pyrolyzer would be effective for the treatment of sediments contaminated with PCDD/PCDF, toxic heavy metals and organic matters simultaneously.     

地衣对重金属的累积效应用于大气监测的初步研究

以采自不同污染区的3个种共18个地衣样本作为试验材料,利用原子吸收分光光度计,测定样品中铅、镉的含量,评估环境质量。结果表明:铅是其中两个样点中的重要沉积物,在各地衣样品中有不同程度的积累,离子积累的浓度与污染源的相对位置具有直接的关系。根据累积浓度不同,可以推测当地的空气质量。     

Using SPMDs to Assess Natural Recovery of PCB-contaminated Sediments in Lake Hartwell,SC: I. A Field Test of New In-Situ Deployment Methods

Results from the field testing of some innovative sampling methods developed to evaluate risk management strategies for polychlorinated biphenyl (PCB) contaminated sediments are presented. Semipermeable membrane devices (SPMDs) were combined with novel deployment methods to quantify the availability of PCBs at the Sangamo-Weston Lake Hartwell Superfund Site in SC. Three locations in Lake Hartwell were examined: a background site (BKG) with little detectable contamination and two contaminated sites (T-M/N and T-O). PCB availability was quantified using sediment surface samplers designed to hold SPMDs in contact with surface sediments, benthic dome samplers designed to enclose and suspend SPMDs at the sediment-water interface, and commercially obtained SPMD cages suspended in the water column. A two-way analysis of variance showed significant effects by sampler type (P < 0.0001) and site (P < 0.0001) for mean time-weighted average (TWA) total PCBs (t-PCBs). Regardless of the SPMD sampler used, mean TWA t-PCBs were directly proportional to the level of contamination present (BKG < T-M/N < T-O). Water column and surface sediment sampler t-PCB uptake patterns were described by a significant linear fit of the data (r² = 0.9625, p < 0.0001, and r² = 0.8188, p < 0.0001, respectively). Dome and sediment surface SPMD samples had a higher percentage of higher chlorinated PCBs compared to water column samples.