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Effectiveness of a Metal Stabilizer When Treating Hazardous Waste with Modified Fenton’s Reagent and Sodium Persulfate

机译:用改性的Fenton试剂和过硫酸钠治疗危险废物时金属稳定剂的有效性

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The effectiveness of a metal stabilizer (a mixture of magnesium oxides and calcium phosphates) was evaluated when treating hazardous waste contaminated soil in conjunction with modified Fenton’s reagent (MFR), sodium persulfate activated by an alkali (ASP), and sodium persulfate activated by MFR (FSP). The soil was contaminated with high concentrations of aromatic hydrocarbons, chlorinated solvents, polychlorinated biphenyls and heavy metals. The objective of the study was to utilize a combination of chemical oxidation and metal stabilization to reduce concentrations of toxicity characteristics leaching procedure (TCLP) of volatile organic compounds (VOCs), primarily benzene, tetrachloroethene (PCE), and 1,2-dichloroethane (DCA) and heavy metals, such as lead and cadmium in soils. To meet the objective, a series of soil-slurry experiments were conducted to first determine the optimum dosage of metal stabilizer needed to treat TCLP metals, followed by evaluation of two doses [i.e. 3% and 5% (w/w)] of MFR, ASP and FSP both in the presence or absence of the metal stabilizer. Treatability results showed that TCLP cadmium and lead were stabilized to non-detectable levels with use of 4% (w/w) metal stabilizer; therefore, the remaining experiments were performed at this concentration. In the absence of metal stabilizer, increases in TCLP lead and cadmium occurred with all tested doses of ASP, FSP and MFR indicating significant metal mobilization. In the presence of metal stabilizer, however, the TCLP lead concentrations decreased significantly to low levels and the degree of TCLP cadmium mobilization decreased with increasing doses of ASP, FSP or MFR showing that the metal stabilizer retains a good portion of its functionality even in the presence of chemical oxidant. When used in conjunction with metal stabilizer, ASP was ineffective and FSP showed substantially decreased treatment of TCLP benzene, PCE and DCA. On the contrary, MFR showed positive results with increased treatment effectiveness of TCLP benzene, PCE and DCA. This is likely due to stabilization of interfering transition metals present in native soils, thereby, limiting hydrogen peroxide wastage. Overall, the results indicate that the metal stabilizer complements the performance of MFR but impedes the performance of systems containing sodium persulfate as it is likely to adversely impact the treatment efficiency of both TCLP VOCs and TCLP metals.
机译:在处理有修饰的Fenton试剂(MFR)的危险废物污染土壤时,评估金属稳定剂(氧化镁和磷酸钙和磷酸钙的混合物),用碱(ASP)激活的钠过硫酸钠和由MFR激活的过硫酸钠(FSP)。土壤污染高浓度的芳烃,氯化溶剂,多氯联苯和重金属。该研究的目的是利用化学氧化和金属稳定化的组合,以减少挥发性有机化合物(VOC),主要苯,四氯乙烯(PCE)和1,2-二氯乙烷(1,2-二氯乙烷)的毒性特征浸出程序(TCLP)的浓度DCA)和重金属,如土壤中的铅和镉。为了满足目标,进行了一系列土壤浆料实验,首先确定治疗TClp金属所需的金属稳定剂的最佳剂量,然后评价两种剂量[即MFR,ASP和FSP的3%和5%(w / w)在存在或不存在金属稳定剂的情况下。处理结果表明,使用4%(w / w)金属稳定剂,将Tclp镉和铅稳定为未检测到的水平;因此,在该浓度下进行剩余的实验。在没有金属稳定剂的情况下,TClP铅和镉的增加,所有测试剂量的ASP,FSP和MFR表示,表明显着的金属摩擦。然而,在金属稳定剂的存在下,TCLP铅浓度显着降低到低水平,并且随着ASP,FSP或MFR的剂量,显示金属稳定剂即使在其功能的良好部分保持良好部分的情况下,TCLP镉剧中程度降低化学氧化剂的存在。当与金属稳定剂结合使用时,ASP无效,FSP显示出TClp苯,PCE和DCA的处理显着降低。相反,MFR显示了TClp苯,PCE和DCA的治疗效果增加了阳性结果。这可能是由于在天然土壤中存在的干扰过渡金属的稳定,从而限制过氧化氢废料。总的来说,结果表明,金属稳定剂补充了MFR的性能,但阻碍了含有过硫酸钠的系统的性能,因为它可能对TClP VOC和TCLP金属的治疗效率产生不利影响。

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