Higgins Thomas E, Halloran Amy R, Dobbins Maribeth E, Pittignano Alex J
a CH2M HILL , Reston , Virginia , USA.
b CH2M HILL , Albuquerque , New Mexico , USA.
J Air Waste Manag Assoc. 1998 Nov;48(11):1100-1106. doi: 10.1080/10473289.1998.10463768.
In investigating chromium sites in New Jersey, it has been observed that an organic-rich 0.5- to 4-foot-thick layer of decayed vegetation (locally known as "meadowmat") underlying the chromium-containing material acts as a natural barrier to the migration of Cr(VI). The groundwater in a sand layer directly beneath the meadowmat has been shown to contain low or nondetectable levels of chromium. The meadowmat is under highly reduced conditions due to bacterial activity associated with the organic material. Based on the observed ability of the meadowmat to reduce Cr(VI) to Cr(III), the feasibility of in situ reduction of Cr(VI) to Cr(III) at chromite ore processing residue (COPR) sites was investigated in biologically-active, laboratory-scale test columns. COPR typically has a high pH (in excess of 12) and may contain total chromium concentrations as high as 70,000 mg/kg. Experimental results demonstrated that the addition of a mineral acid (to lower the pH to between 7.0 and 9.5) and a bacteria-rich organic substrate (fresh manure) resulted in the reduction of Cr(VI) to the less toxic and less mobile trivalent form. Pore water Cr(VI) was reduced from approximately 800 mg/L to less than 0.05 mg/L over a period of eight months. This is less than the U.S. Environmental Protection Agency's (EPA) Maximum Contaminant Level (MCL) for chromium in drinking water of 0.1 mg/L. Solid phase Cr(VI) concentrations decreased from approximately 2,000 mg/kg to less than 10 mg/kg in the columns over a period of 11 months while the total chromium concentrations remained unchanged. Toxicity Characteristic Leaching Procedure (TCLP) extract from the treated columns met the regulatory limit of 5 mg/L of Cr, whereas the untreated samples had TCLP extract concentrations greater than 40 mg/L. This study demonstrated the potential applicability of in situ reduction to soils contaminated with Cr(VI) by adjusting the pH to between 7.0 and 9.5 and mixing in a bacteria-rich organic substrate.
在对新泽西州的铬污染场地进行调查时,人们观察到,含铬物质下方有一层0.5至4英尺厚、富含有机物的腐烂植被层(当地称为“草甸垫”),它对六价铬的迁移起到了天然屏障的作用。草甸垫正下方砂层中的地下水已被证明含有低水平或未检测到的铬。由于与有机物质相关的细菌活动,草甸垫处于高度还原的条件下。基于观察到的草甸垫将六价铬还原为三价铬的能力,在具有生物活性的实验室规模试验柱中,研究了在铬铁矿加工残渣(COPR)场地将六价铬原位还原为三价铬的可行性。COPR的pH值通常较高(超过12),总铬浓度可能高达70000mg/kg。实验结果表明,添加无机酸(将pH值降至7.0至9.5之间)和富含细菌的有机底物(新鲜粪肥)可使六价铬还原为毒性较小、迁移性较低的三价形式。在八个月的时间里,孔隙水中的六价铬从约800mg/L降至低于0.05mg/L。这低于美国环境保护局(EPA)规定的饮用水中铬的最大污染物水平(MCL)0.1mg/L。在十一个月的时间里,试验柱中固相六价铬浓度从约2000mg/kg降至低于10mg/kg,而总铬浓度保持不变。处理后试验柱的毒性特性浸出程序(TCLP)提取物符合铬含量5mg/L的监管限值,而未处理样品的TCLP提取物浓度大于40mg/L。这项研究表明,通过将pH值调节至7.0至9.5之间并混入富含细菌的有机底物,原位还原法对被六价铬污染的土壤具有潜在的适用性。