Cr (VI) heavy polluted site in-situ detoxification method based on biogas residue

一种六价铬、重污染的技术,应用在污染的土壤的复原、化学仪器和方法、土壤调节材料等方向,能够解决硫酸盐二次污染、有腐蚀性、土壤酸化等问题,达到避免二次污染、自然耐受力强的效果

Pending Publication Date: 2016-09-21
QINGDAO TECHNOLOGICAL UNIVERSITY
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

At present, the mainstream technology of chromium-containing soil is to use ferrous sulfate to reduce hexavalent chromium, but the pH of ferrous sulfate is too low, it is corrosive, and it is easy to be oxidized and deactivated in the air. Therefore, the reduction of hexavalent chromium can only be short-term, not long-term reduction
In order to effectively treat chromium-containing soil, it is often necessary to add excessive ferrous sulfate, which is likely to cause secondary pollution of sulfate radicals
Patent No. 201410101586.0 introduces a method of using ferrous sulfate to repair Cr(VI)-containing sites in situ. Since ferrous is easy to oxidize and fail in the air, this method uses low pH citric acid to inhibit its oxidation and increase the penetration of ferrous , but correspondingly increases the cost, and makes the soil acidified, and still brings secondary pollution of sulfate
Patent No. 201310642919.6 introduces a method of using organic waste to repair Cr(VI)-containing sites in situ. This is a low-cost method for disposing of hexavalent chromium soil, but this method is easy to cause bacterial contamination through natural infiltration. Closure at a certain section of the soil, resulting in the failure of the bacterial solution to be transported and the organic matter and dissolved hexavalent chromium solution entering the groundwater, causing secondary pollution of the groundwater
[0003] Generally speaking, for sites polluted with high concentration of hexavalent chromium, it is difficult to fully restore traditional chemical reagents, while microbial reducing bacteria agents are easily killed by high concentration of hexavalent chromium and lose their effect

Method used

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Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0020] (1) Mix sodium sulfate, biogas residue or carbon source solution according to a certain ratio, so that the dry biogas residue content of the mixed solution is 0.1-5%, the solid content is 0.5-5%, the organic carbon content is 0.5-5%, and the sulfate (in SO4 record) / organic carbon mass ratio is 0.1: 1, the solution biochemical reaction after mixing is 1 day, after passing through 100 mesh sieves, obtain chromium soil remediation agent;

[0021] (2) Ferrous sulfate solution is injected into the field by injection well pressurized injection mode, when injection pressure exceeds 1MPa, stop injecting ferrous sulfate solution;

[0022] (3) After an interval of 2 days, the repairing bacteria agent in the step (1) is continuously input into the chromium-containing soil through the pressurized injection mode of the injection well, and when the injection pressure is greater than 1MPa, the injection is stopped;

[0023] (4) Repeat the pressurized injection every 5-10 days, and sto...

Embodiment 2

[0026] (1) Mix potassium sulfate, biogas residue or carbon source solution according to a certain ratio, so that the dry biogas residue content of the mixed solution is 5-20%, the solid content is 5-25%, the organic carbon content is 5-25%, and the sulfate (in SO4 record) / organic carbon mass ratio is 0.5: 1, the solution biochemical reaction after mixing is 2 days, obtains chromium soil remediation agent;

[0027] (2) Ferrous sulfate solution is injected into the site by injection well pressurized injection mode, and when injection pressure exceeds 0.5MPa, stop injecting ferrous sulfate solution;

[0028] (3) After an interval of 1 day, the repairing bacteria agent in the step (1) is continuously input into the chromium-containing soil through the pressurized injection mode of the injection well, and when the injection pressure is greater than 1MPa, the injection is stopped;

[0029] (4) During the restoration period, the soil moisture content of the site is required to be wit...

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Abstract

The invention provides a Cr (VI) heavy polluted soil in-situ restoration method. According to the method, firstly, a chemical reduction agent is injected into soil in situ; high-concentration Cr (VI) is subjected to primary reduction, so that the high-concentration hexavalent Cr cannot generate a toxic effect on the subsequent microorganism ecologic microbial inoculum; then, biogas residue, a carbon source and sulphate are prepared into the ecologic microbial inoculum to be injected into the Cr-containing soil in situ in a pressurizing way; by adopting a special maintenance mode, a large-scale reduction buffer belt containing sulphate reduction bacteria and sulfides is formed in the underground soil of a site; and the Cr (VI) is continuously and effectively reduced. The method has the advantages that the hexavalent Cr can be effectively reduced, and meanwhile, the cost is reduced.

Description

technical field [0001] The invention provides a method for in-situ remediation of heavily polluted Cr(VI)-contaminated soil. Firstly, a chemical reducing agent is injected into the soil in situ, and then biogas residue, carbon source and sulfate are formulated into medicaments and injected in situ under pressure. In the chromium-containing soil, a special maintenance method is adopted to form a large-scale reduction buffer zone containing sulfate-reducing bacteria and sulfide in the underground soil of the site to continuously and effectively reduce hexavalent chromium. The method can efficiently reduce hexavalent chromium while saving costs, and belongs to the field of environmental protection. Background technique [0002] Chromium and its compounds are commonly used basic raw materials in metallurgy, metal processing, electroplating, tanning, paint, pigment and other industries. During the production process of the above industries, a large amount of chromium-containing w...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): B09C1/08
CPCB09C1/08B09C2101/00B09C1/10B09C1/002C09K17/48
Inventor 张大磊李瑞栋孙箫赵昱皓
Owner QINGDAO TECHNOLOGICAL UNIVERSITY
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