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Alkaline chromium-contaminated soil solidifying, stabilizing and repairing method

A remediation method and technology for chromium pollution, applied in the field of environmental engineering, can solve problems such as being unsuitable for large-scale application, serious secondary pollution, poor treatment effect, etc., to achieve efficient and fast resource utilization, reduce treatment costs, and improve treatment. The effect of efficiency

Active Publication Date: 2016-04-20
海南碧天环境工程技术有限公司
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0005] The application of Chinese Patent Publication No. CN102228901A adopts adding ferrous salt solution to chromium-contaminated soil to reduce hexavalent chromium to trivalent chromium, and then add lime solution to convert trivalent chromium into chromium hydroxide. The main problem is that the treatment effect is not good. Good, poor long-term stability, etc.
[0006] The application of Chinese Patent Publication No. CN201310493630.2 adopts the method of adding iron powder or sodium metabisulfite or a mixture of the two under acidic conditions to rinse the chromium pollution, which has the problems of serious secondary pollution, poor treatment effect and high cost.
[0007] The application of Chinese Patent Publication No. CN201210355258.4 uses microbial methods to repair the soil. There are mainly steps such as long fermentation period, certain requirements for initial concentration, and activation and cultivation of bacteria. The operation is relatively complicated and is not suitable for large-scale Applications
However, there are few studies on the solidification and stabilization methods of chromium-contaminated soils. Due to the strong migration of hexavalent chromium, the general solidification and stabilization methods have poor applicability.
At the same time, the existing chromium-contaminated soil treatment technology is relatively backward, resulting in low restoration efficiency, high cost, secondary pollution and environmental risks of chromium-contaminated soil

Method used

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Examples

Experimental program
Comparison scheme
Effect test

Embodiment example 1

[0052] Weigh 100kg of chromium-contaminated soil, measure the water content by drying method and calculate the dry basis weight of chromium-contaminated soil to be 85kg, and the total chromium concentration in the chromium-contaminated soil is 3547mg / kg through chemical analysis. Add 100kg of tap water to 100kg of chromium-contaminated soil, form mud after stirring for 30 minutes, use plate and frame press filter to carry out solid-liquid separation to mud, form filter soil and filtrate, adopt spectrophotometry to test the concentration and content of hexavalent chromium in the filtrate, The concentration of hexavalent chromium in the filtrate is 12.3mg / L, add sulfuric acid solution in the filtrate, adjust the pH of the filtrate to be 4, then add CaS 5 , CaS 5 The molar ratio of hexavalent chromium to the filtrate is 3:1, and the filtrate is evenly stirred for 30 minutes, and the filter soil separated from solid and liquid is added and mixed evenly, and blast furnace slag and ...

Embodiment example 2

[0055] Weigh 100kg of chromium-contaminated soil, measure the water content by drying method and calculate the dry basis weight of chromium-contaminated soil to be 90kg, and the total chromium concentration in the chromium-contaminated soil is 1257mg / kg through chemical analysis. Add 150 kg of river water to 100 kg of chromium-contaminated soil, stir for 30 minutes to form mud, use plate and frame press to separate the mud from solid to liquid to form filter soil and filtrate, and use spectrophotometry to test the concentration and content of hexavalent chromium in the filtrate. The concentration of hexavalent chromium in the filtrate is 6.5mg / L, add sulfuric acid solution in the filtrate, adjust the pH of the filtrate to be 5, then add CaS 5 , CaS 5 The molar ratio of hexavalent chromium to the filtrate is 3:1, and the filtrate is uniformly stirred for 30 minutes, and the filter soil for solid-liquid separation is added and mixed evenly, and blast furnace slag and active magn...

Embodiment example 3

[0058] Weigh 100kg of chromium-contaminated soil, measure the moisture content by drying method and calculate the dry basis weight of chromium-contaminated soil to be 95kg, and the total chromium concentration in the chromium-contaminated soil is 1941mg / kg through chemical analysis. Add 200 kg of tap water to 100 kg of chromium-contaminated soil, stir for 30 minutes to form mud, and use centrifugation to separate the mud from solid to liquid to form filter soil and filtrate. Use spectrophotometry to test the concentration and content of hexavalent chromium in the filtrate. The concentration of hexavalent chromium is 7.4mg / L, add sulfuric acid solution to the filtrate, adjust the pH of the filtrate to 6, then add CaS5, CaS 5 The molar ratio of hexavalent chromium in the filtrate is 3:1, and the filtrate is uniformly stirred for 30 minutes, and the filter soil for solid-liquid separation is added and mixed uniformly, and blast furnace slag and active magnesium oxide are added to ...

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PUM

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Abstract

The invention relates to an alkaline chromium-contaminated soil solidifying, stabilizing and repairing method, and belongs to the technical field of environmental engineering. Hexavalent chromium in chromium-contaminated soil is separated into water by adopting water-washing pretreatment; hexavalent chromium-contaminated water is adjusted to be acid by adopting sulfuric acid as an acidifying or alkalizing agent, therefore, a reduction reaction of hexavalent chromium is facilitated, sulfuric acid can participate in a later curing reaction, and high-valued application of sulfuric acid is achieved; the efficiency of reducing hexavalent chromium in the contaminated water into trivalent chromium is improved by adopting CaS5 as a reducing agent, and water-washed soil and water after the reduction treatment are mixed for solidification and stabilization treatment; resource utilization of blast furnace slag is achieved by adopting the blast furnace slag and active magnesium oxide as solidification materials, enhancing of the strength of the solidified soil and wrapping of contaminants can be quickly achieved, and the long-term stability of the treated chromium-contaminated soil is good. The method has the advantages of being low in treatment cost, good in effect, free of secondary pollution, convenient to operate, good in long-term stability, high in resource utilization and the like.

Description

technical field [0001] The invention belongs to the technical field of environmental engineering, and in particular relates to a method for stabilizing alkaline chromium-contaminated soil. Background technique [0002] At present, there are more than 20 sites left over from the shutdown of chromium salt factories, more than 40 sites for storing chromium slag left over from history, sites of thousands of electroplating (chrome plating) companies, and sites of hundreds of tanning companies in China. However, only a few small-scale sites in China have carried out soil pollution control work, and the pollution status of typical sites is very serious, and chromium-contaminated sites not only pollute soil, but also pollute groundwater. With the acceleration of urbanization and industrialization, more and more land is polluted by chromium, and the strategic layout of cities is readjusted. A large number of chromium-polluted sites are in urgent need of treatment. Soil chromium poll...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): B09C1/00
CPCB09C1/00
Inventor 户园凌
Owner 海南碧天环境工程技术有限公司
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