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首页> 外文期刊>Water, Air and Soil Pollution: Focus. >REMEDIATION OF SOIL AND GROUND WATER CONTAMINATED WITH PAH USING HEAT AND FE(II)-EDTA CATALYZED PERSULFATE OXIDATION
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REMEDIATION OF SOIL AND GROUND WATER CONTAMINATED WITH PAH USING HEAT AND FE(II)-EDTA CATALYZED PERSULFATE OXIDATION

机译:热和Fe(II)-EDTA催化过硫酸盐氧化修复PAH污染的土壤和地下水

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摘要

The feasibility of degrading 16 USEPA priority polycyclic aromatic (PAH) hydrocarbons (PAHs) with heat and Fe(II)-EDTA catalyzed persulfate oxidation was investigated in the laboratory. The experiments were conducted to determine the effects of temperature (i.e. 20 °C, 30 °C and 40 °C) and iron-chelate levels (i.e., 250 mg/L-, 375 mg/L- and 500 mg/L-Fe(II)) on the degradation of dissolved PAHs in aqueous systems, using a series of amber glass jars as the reactors that were placed on a shaker inside an incubator for temperature control. Each experiment was run in duplicate and had two controls (i.e., no persulfate in systems). Samples were collected after a reaction period of 144 hrs and measured for PAHs, pH and sodium persulfate levels. The extent of degradation of PAHs was determined by comparing the data for samples with the controls.The experimental results showed that persulfate oxidation under each of the tested conditions effectively degraded the 16 target PAHs. All of the targeted PAHs were degraded to below the instrument detection limits (~4 mu g/L) from a range of initial concentration (i.e., 5 mu g/L for benzo(a)pyrene to 57 mu g/L for Phenanthrene) within 144 hrs with 5 g/L of sodium persulfate at 20 °C, 30 "C and 40 CC. The data indicated that the persulfate oxidation was effective in degrading the PAHs and that external heat and iron catalysts might not be needed for the degradation of PAHs.The Fe(II)-EDTA catalyzed persulfate also effectively degraded PAHs in the study. In addition, the data on the variation of persulfate concentrations during the experiments indicated that Fe(II)-EDTA accelerated the consumption of persulfate ions.The obtained degradation data cannot be used to evaluate the influence of temperature and Fe(II) levels on the PAH degradation because the PAHs under each of the tested conditions were degraded to below the instrument detection limit within the first sampling point. However, these experiments have demonstrated the feasibility of degrading PAHs in aqueous systems with persulfate oxidation. Additional tests are being conducted to evaluate the effectiveness of treating PAHs in soils and obtaining the rate of degradation of PAHs with persulfate oxidation.Two sets of laboratory experiments were conducted to evaluate the ability of sodium persulfate in oxidizing real world PAH-contaminated soils collected from a Superfund site in Connecticut. The first set of soil sample were treated only with persulfate and to the second batch, mixture of persulfate and Fe(H)-EDTA solutions were added. The results of the second test showed that within 24 hours, 75% to 100% of the initial concentrations of seven PAH compounds detected in the soil samples were degraded by sodium persulfate mixed with FE(H)-EDTA.
机译:在实验室中研究了通过加热和Fe(II)-EDTA催化过硫酸盐氧化降解16种USEPA优先多环芳烃(PAH)的可行性。进行实验以确定温度(即20°C,30°C和40°C)和螯合铁水平(即250 mg / L-,375 mg / L-和500 mg / L-Fe)的影响(II))关于溶解的多环芳烃在水性系统中的降解,使用一系列琥珀色玻璃瓶作为反应器,将其放置在培养箱内的振荡器上进行温度控制。每个实验一式两份进行,并有两个对照(即系统中没有过硫酸盐)。在144小时的反应时间后收集样品,并测量PAH,pH和过硫酸钠的水平。通过比较样品和对照的数据确定PAHs的降解程度。实验结果表明,在每种测试条件下过硫酸盐的氧化都能有效降解16种目标PAHs。从目标浓度(即苯并(a)py的浓度为5微克/升,菲为57微克/升)中,所有目标多环芳烃均被降解至低于仪器检测极限(〜4微克/升)。在20°C,30“ C和40 CC下用5 g / L过硫酸钠在144小时内。数据表明,过硫酸盐氧化可有效降解PAHs,降解可能不需要外部热和铁催化剂Fe(II)-EDTA催化过硫酸盐也能有效降解PAHs。此外,实验过程中过硫酸盐浓度变化的数据表明Fe(II)-EDTA加速了过硫酸盐离子的消耗。获得的降解数据不能用于评估温度和Fe(II)含量对PAH降解的影响,因为在每个测试条件下,PAH均在第一个采样点内降解至仪器检测极限以下。德蒙斯特拉提出了用过硫酸盐氧化降解水性体系中多环芳烃的可行性。还进行了其他测试,以评估在土壤中处理PAHs的有效性并获得过硫酸盐氧化降解PAHs的速率。进行了两组实验室实验,以评估过硫酸钠对从土壤中收集的PAH污染的真实土壤的氧化能力康涅狄格州的超级基金网站。第一组土壤样品仅用过硫酸盐处理,第二批中加入过硫酸盐和Fe(H)-EDTA溶液的混合物。第二次测试的结果表明,在土壤样品中检测到的7种PAH化合物初始浓度的75%至100%被过硫酸钠与FE(H)-EDTA混合降解了。

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