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Combined leaching-stabilization rehabilitation method for soil contaminated by chromium residue

A technology of combined restoration of polluted soil, which is applied in the field of soil pollution treatment, can solve problems such as the difficulty in achieving the time required for the reaction between the reducing agent and soil hexavalent chromium, incomplete reduction of hexavalent chromium, and the increase in the amount of reducing agent used to solve the problem of soil pollution. Severe matrix loss, reduced leaching water consumption, and short time

Inactive Publication Date: 2019-03-12
BEIJING GEOENVIRON ENG & TECH
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

The reducing agent is sprayed on the surface of the soil mound in the same way in the later stage of rinsing: on the one hand, in the process of spraying the compound bacterial solution in the early stage, it is easy to form a dominant flow channel in the soil mound, which leads to the contact between the reducing agent sprayed in the later stage and the pollutants in the soil The efficiency is low; on the other hand, the reducing agent flows through the surface of the polluted soil from top to bottom, and the residence time is short, so it is difficult to reach the time required for the reaction between the reducing agent and the hexavalent chromium in the soil
The amount of reducing agent is greatly increased, and the reduction of hexavalent chromium remaining in the soil is not complete

Method used

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  • Combined leaching-stabilization rehabilitation method for soil contaminated by chromium residue

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Experimental program
Comparison scheme
Effect test

Embodiment 1

[0032] like figure 1 Shown:

[0033] (1) Restoration preparation: Excavation and transfer of chromium slag-contaminated soil, crushing and screening, construction of leachate drainage structure, soil heaping, etc. The concentration of hexavalent chromium in the soil sample selected in this embodiment is 5670.3 mg / kg, and the content of hexavalent chromium in the leachate is 122.7 mg / L. This embodiment is carried out in a 1000L beef tendon vat. The size of the beef tendon vat is 140 cm in diameter and 75 cm in height. There is a discharge port at the bottom, and the discharge of the leachate is controlled by a switch. Firstly, gravel is laid on the bottom of the vat to form a leachate drainage structure, and the thickness of the gravel layer is 15cm. The soil is piled on top of the crushed stone layer, naturally accumulated, with a thickness of 55cm.

[0034] (2) Rinse repair: After the repair preparation process is completed, prepare a eluent consisting of 7 parts by mass o...

Embodiment 2

[0037] like figure 1 Shown:

[0038] (1) Restoration preparation: Excavation and transfer of chromium slag-contaminated soil, crushing and screening, construction of leachate drainage structure, soil heaping, etc. The concentration of hexavalent chromium in the soil sample selected in this embodiment is 3244.2 mg / kg, and the content of hexavalent chromium in the leachate is 126.4 mg / L. This embodiment is carried out in a 1000L beef tendon vat. The size of the beef tendon vat is 140 cm in diameter and 75 cm in height. There is a discharge port at the bottom, and the discharge of the leachate is controlled by a switch. Firstly, gravel is laid on the bottom of the vat to form a leachate drainage structure, and the thickness of the gravel layer is 15cm. The soil is piled on top of the crushed stone layer, naturally accumulated, with a thickness of 55cm.

[0039] (2) Rinse repair: After the repair preparation process is completed, prepare a eluent consisting of 5 parts of GLDA, ...

Embodiment 3

[0042] like figure 1 Shown:

[0043] (1) Restoration preparation: Excavation and transfer of chromium slag-contaminated soil, crushing and screening, construction of leachate drainage structure, soil heaping, etc. The concentration of hexavalent chromium in the soil sample selected in this embodiment is 4340.2 mg / kg, and the content of hexavalent chromium in the leachate is 86.4 mg / L. This embodiment is carried out in a 1000L beef tendon vat. The size of the beef tendon vat is 140 cm in diameter and 75 cm in height. There is a discharge port at the bottom, and the discharge of the leachate is controlled by a switch. Firstly, gravel is laid on the bottom of the vat to form a leachate drainage structure, and the thickness of the gravel layer is 15cm. The soil is piled on top of the crushed stone layer, naturally accumulated, with a thickness of 55cm.

[0044] (2) Rinse repair: After the repair preparation process is completed, prepare a eluent consisting of 6 parts of GLDA, 1...

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Abstract

The invention discloses a combined leaching-stabilization rehabilitation method for soil contaminated by chromium residue. The method specifically comprises the following steps: remediation preparation, specifically, a leachate guide drainage structure is constructed, and the soil contaminated by the chromium residue is dredged, transported, broken, screened and piled; leaching remediation, specifically, a leaching agent is evenly distributed on the surface of a soil heap, the leaching agent separates chromium contaminants in the soil from top to bottom, a discharge port of the leachate is opened and the leachate is collected to a detoxification tank, hexavalent chromium is reduced and trivalent chromium is precipitated, and supernatant is used for circulating spray; and stabilization rehabilitation, specifically, the discharge port of the leachate is closed, stabilizer solution is added to a leaching tank until the soil is submerged, and the chromium contaminants remaining in the stabilized soil are soaked and stabilized by the stabilizer. By means of the combined leaching-stabilization rehabilitation method for the soil contaminated by the chromium residue, the leaching process and the stabilization process are organically combined, first, the total amount of the contaminants in the soil contaminated by chromium residue is reduced by spraying the leaching agent, and then theresidual contaminants are further removed by soaking the stabilizer, so that the amount of stabilizer addition is greatly reduced, and the environmental risk of the soil contaminated by the chromium residue is effectively eliminated.

Description

technical field [0001] The invention relates to the technical field of soil pollution treatment, in particular to a leaching-stabilization combined restoration method for soil polluted by chromium slag. Background technique [0002] Chromium salt is one of the main series products of inorganic chemical industry. It is widely used in chemical industry, metallurgy, prevention and machinery and other industries. About 15% of the products in my country's national economy are related to chromium salt. The traditional method of chromium salt production mainly adopts high-temperature roasting-water immersion-multi-stage evaporation crystallization process, the extraction rate of chromium salt is only about 75%, and 2.5-3.0t of chromium residue is discharged for every 1t of chromium salt product produced. 1.0%~3.0% water-soluble Na2CrO contained in chromium slag 4 and 1.0% to 1.5% acid-soluble CaCrO 4 It is the main component of environmental pollution. With the in-depth implemen...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): B09C1/02B09C1/08
CPCB09C1/02B09C1/08
Inventor 吕正勇范吉强方华祥郭明达李来顺
Owner BEIJING GEOENVIRON ENG & TECH
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