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    • 1. 发明授权
    • Process for the remediation of contaminated particulate material
    • 污染颗粒材料的修复方法
    • US5436384A
    • 1995-07-25
    • US137457
    • 1993-10-18
    • David C. GrantEdward J. LahodaC. P. Keegan
    • David C. GrantEdward J. LahodaC. P. Keegan
    • G21F9/28B03B9/00B09C1/00B09C1/02G21F9/30G21F9/00
    • B03B9/00B09C1/02G21F9/30
    • A method for segregating fines from the clean coarse fraction of the soil, preparing the contaminated fines for subsequent processing, and then separating the contaminants from the clean fines. The process produces a small, highly concentrated contaminanth fraction and a large fraction of clean soil. Metals, metallic compounds, and/or radioactive contaminants are removed from the fine fraction using either gravity separation, multistage gravity separation, a centrifugal jig, regular magnetic or paramagnetic separation using a high gradient magnetic separator, and/or a superconducting separator. Preparation of the fines requires selective segregation of the targeted particles size range and the removal of interfering soil fractions, and vegetation such as root hairs. This preparation is accomplished by a combination of attrition scrubbing, countercurrent jigging, and screening.
    • 一种将细粒与干净的粗糙部分分离的方法,为污染的细粉制备后续加工,然后将污染物与干净的细粉分离。 该过程产生小的,高度浓缩的污染物部分和大部分清洁的土壤。 和/或超导分离器,使用重力分离,多级重力分离,离心夹具,常规磁性或顺磁性分离法,从精细馏分中除去金属,金属化合物和/或放射性污染物。 细粉的制备需要选择性分离目标颗粒尺寸范围和去除干扰的土壤部分,以及植被如根毛。 该制备通过磨擦擦洗,逆流夹击和筛选的组合来实现。
    • 3. 发明授权
    • Method and apparatus for cleaning contaminated particulate material
    • 清洁污染颗粒物的方法和设备
    • US5268128A
    • 1993-12-07
    • US648673
    • 1991-01-31
    • Edward J. LahodaDavid C. Grant
    • Edward J. LahodaDavid C. Grant
    • B09C1/02G21F9/04G21F9/00B03B5/28
    • B09C1/02G21F9/04
    • Particulate material is treated by first washing the contaminated material with a contaminant mobilizing solution comprising a leaching agent, a surfactant or a mixture thereof. Large particles, typically greater than 5 mm are mechanically separated, washed with water and returned to the site as recovered soil. Fines, along with contaminants dissolved or dispersed in the contaminant mobilizing solution are separated from intermediate sized particles by a countercurrent flow of the contaminant mobilizing solution, preferably in a mineral jig. The intermediate sized particles are then abraded in an attrition scrubber to dislodge attached mineral slimes or fines. These additional fines are separated from the intermediate sized particles with a countercurrent flow of wash water in a second mineral jig. The preferred oxidizing agent is chlorine, and hydrogen is the preferred reducing agent.
    • 通过首先用包含浸出剂,表面活性剂或其混合物的污染物移动溶液洗涤被污染的材料来处理颗粒材料。 通常大于5mm的大颗粒机械分离,用水洗涤并作为回收的土壤返回到现场。 细粉以及溶解或分散在污染物移动溶液中的污染物通过污染物移动溶液的逆流流动,优选在矿物夹具中与中等尺寸的颗粒分离。 然后在磨耗洗涤器中研磨中等尺寸的颗粒以除去附着的矿物质泥或细粒。 这些额外的细粉与中等尺寸的颗粒分离,在第二矿物夹具中具有逆流的洗涤水。 优选的氧化剂是氯,氢是优选的还原剂。
    • 8. 发明授权
    • Removal or organics and volatile metals from soils using thermal
desorption
    • 使用热解释的土壤中的去除或有机金属和挥发性金属
    • US5230167A
    • 1993-07-27
    • US785397
    • 1991-10-30
    • Edward J. LahodaDavid C. Grant
    • Edward J. LahodaDavid C. Grant
    • A62D3/00B09C1/00B09C1/06F26B25/00
    • F26B25/006B09B3/0091B09C1/06
    • The removal of organics and volatile metals from soils using thermal desorption comprises moving contaminated materials, positioned on a belt conveyor, through a chamber under oxygen conditions, temperature conditions, and residence time effective to substantially avoid incineration of the contaminants. The method further comprises heating the contaminated material for volatilizing the contaminants and for producing a processed material that is substantially decontaminated. To carry the volatilized contaminants from the chamber, a transport gas may be passed through the chamber counter-current to the movement of the contaminated material. A gas stream including the volatilized contaminants and the transport gas may be passed through a condenser and through a scrubber for producing a substantially cleaned gas and a contaminated liquid concentrate. The cleaned gas may be recycled back into the chamber as the transport gas or passed through a gas cleaning system prior to discharge into the atmosphere. The liquid concentrate is passed through a water treatment system for producing substantially cleaned water. The water may be passed through an air cooler and recycled back into the quencher or may be passed through a carbon absorption column and recycled as quench water for the processed material.
    • 9. 发明授权
    • Method for remediating soil containing radioactive contaminants
    • 补救含有放射性污染物的土壤的方法
    • US5640701A
    • 1997-06-17
    • US997076
    • 1992-12-29
    • David C. GrantEdward J. LahodaAlbert J. Dietrich
    • David C. GrantEdward J. LahodaAlbert J. Dietrich
    • B09C1/02G21F9/28G21F9/00
    • B09C1/02G21F9/28
    • Soil comprising small soil particles, clay and silt particles, humus, fine vegetation, and contaminated with soluble or insoluble radioactive species is treated by first introducing an aqueous extracting solution comprising a mixture of sodium and potassium carbonate (or bicarbonate), or ammonium carbonate (or bicarbonate) into the soil to solubilize and disperse the radioactive species into solution. The extracting solution has a pH greater than or equal to about 7.5. Contaminated fine vegetation then is separated from the soil and extracting solution. Next, an acid like hydrochloric acid is introduced into the soil. The acid is added in an amount sufficient to lower the pH of the extracting solution at which point desirable organic material will substantially precipitate or coagulate from the extracting solution. The cleansed soil particles, including organic matter, is separated from the contaminated extracting solution. Radioactive species are then removed from the extracting solution, which then may be reused.
    • 通过首先引入包含碳酸钠和碳酸钾(或碳酸氢钠)或碳酸铵(或碳酸氢钠)的混合物的水提取溶液来处理包含小的土壤颗粒,粘土和粉砂颗粒,腐殖质,细小植被和被可溶性或不溶性放射性物质污染的土壤 或碳酸氢盐)放入土壤中以将放射性物质溶解并分散到溶液中。 提取液的pH值大于或等于约7.5。 污染好的植被然后与土壤和提取液分离。 接下来,将酸如盐酸引入土壤中。 加入的酸的量足以降低萃取溶液的pH值,此时所需的有机物质将从萃取溶液基本上沉淀或凝结。 清洁的土壤颗粒(包括有机物质)与污染的提取溶液分离。 然后从提取溶液中除去放射性物质,然后可以重复使用。