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Method and device for biochemically recharging and restoring polluted soils in chromium slag yard

A technology for polluted soil and chromium slag storage yard, applied in the field of environmental engineering, can solve the problems of unreported engineering remediation of chromium-contaminated soil, harsh soil conditions by electric remediation method, secondary soil pollution, etc. The effect of restoring and improving soil physicochemical properties and easily controllable conditions

Active Publication Date: 2010-09-15
CENT SOUTH UNIV
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

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Problems solved by technology

However, these methods have their own limitations: the cost of immobilization / stabilization method is high, and the treatment effect is not good; the chemical reduction method is easy to cause secondary pollution of the soil, and how to remove the hexavalent chromium in the soil is the key to this technology. Difficulties; the chemical cleaning method is only suitable for soil with a large permeability coefficient (such as sandy soil, etc.), and it is easy to cause secondary pollution of the soil when the cleaning solution is introduced; the electrodynamic repair method has strict requirements on soil conditions and expensive repair costs
Although many Cr(VI)-reducing bacteria have been isolated, there is no report on the engineering restoration of chromium-contaminated soil

Method used

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  • Method and device for biochemically recharging and restoring polluted soils in chromium slag yard
  • Method and device for biochemically recharging and restoring polluted soils in chromium slag yard
  • Method and device for biochemically recharging and restoring polluted soils in chromium slag yard

Examples

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Effect test

Embodiment 1

[0037] Example 1: Soil remediation of chromium slag yard of Minmetals (Hunan) Ferroalloy Co., Ltd.

[0038] The soil under the chromium slag yard of Minmetals (Hunan) Ferroalloy Co., Ltd. is crushed into soil clods smaller than 2cm through a jaw crusher with a 2cm rolling screen, and transferred to a soil tank of 5.0×4.0×1.0m (Leave an opening with a diameter of 15cm in the lower part of the soil tank), and build a 25-ton (5.0×4.0×0.8m) mound. The flow rate is 1.5m 3 / h alkali-resistant pump pumps the cultivated Pannonibacter phragmitetusBB bacteria solution to spray the soil, and the spray intensity is 0.011m 3 / h.m 2 , collect the leachate from the opening of the soil tank in a volume of 0.5m 3 Intermediate pool of cubic meters with a flow rate of 1.5m 3 / h alkali-resistant pump pumps the leachate from the intermediate pool to a volume of 4m 3 Biochemical reaction is carried out in the biochemical pool, and the bacterial solution of the biochemical pool is extracted to ...

Embodiment 2

[0042] Example 2: Remediation of Chromium Slag Contaminated Soil in Shuangfeng County

[0043] For the chromium slag-contaminated soil in Shuangfeng County, the soil particles were broken into clods smaller than 2cm by using a jaw crusher with a 2cm rolling sieve, and transferred to a soil trough of 5.0×4.0×1.0m (the bottom of the trough left a diameter of 15cm opening), build a 25-ton (5.0×4.0×0.8m) mound. The flow rate is 1.5m 3 The alkali-resistant pump pumped out the cultured Pannonibacter phragmitetus BB to spray the soil with an alkali-resistant pump at a spray intensity of 0.011m 3 / h.m 2 , collect the leachate from the opening of the soil tank in a volume of 0.5m 3 Intermediate pool of cubic meters with a flow rate of 1.5m 3 / h alkali-resistant pump pumps the leachate from the intermediate pool to a volume of 4m 3 Biochemical reaction is carried out in the biochemical pool, and the bacterial solution of the biochemical pool is extracted to circulate and spray the ...

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Abstract

The invention discloses method and device for biochemically recharging and restoring polluted soils in a chromium slag yard. The device comprises a soil treatment groove containing soils to be treated, a middle pond, a biochemical pond and a bacteria culture pond. Every two parts are connected through a water pipe, chromium polluted soils are installed in the soil treatment groove to be heaped after being crushed by a 2cm sieve, the height of a mound is smaller than 0.8m, and the soils are sprayed by Cr (VI) reducing bacteria (Pannonibacter phragmitetus BB) culture medium with the spraying strength of 0.008-0.015m<3> / h.m<2>; and leachate is collected from the bottom of a soil groove to the middle pond, bacterial liquid in the middle pond is pumped into the biochemical pond by an alkali resistance pump, and bacterial liquid in the biochemical pond circulates again to be used for spraying the soils and is in circulating spraying for 5-7 days until the soil leachate does not contain Cr (VI). By adopting the invention to restore the polluted soils in the chromium slag yard, the removal rate of water-soluble Cr (VI) in the soils achieves 99 percent, and the concentration of Cr (VI) leaching toxicity in the soils after restoring is lower than 0.5mg / L and achieves a standard limited value of roadbed materials and concrete aggregates in Technical Specifications for Chromium Slag Pollution Control (HJ / T301-2007). Simultaneously, the invention has the advantages of having simple technology, low cost and no secondary pollution, improving the physicochemical property of the soils, and the like.

Description

technical field [0001] The invention belongs to the field of environmental engineering, and in particular relates to a method and device for remediating chromium-contaminated soil, in particular to a biochemical recharge method and device for remediating heavily polluted soil in chromium slag yards. Background technique [0002] Chromium pollution is a serious environmental problem in my country. Its pollution mainly comes from the discharge of a large amount of waste residue and waste water in industries such as chromium salt, electroplating, tanning, fuel, pigment and organic synthesis. As far as chromium salt production is concerned, there are 63 sites in 24 provinces (municipalities directly under the Central Government) that have chromium salt production plants, of which 18 are still in production; 27 have been closed or bankrupt but still have chromium slag; 18 companies have gone bankrupt or closed down, and chrome slag has been disposed of. More than 12.5-15 million...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): B09C1/10
Inventor 杨志辉柴立元高晓竹彭兵闵小波王兵杨卫春王海鹰李航彬
Owner CENT SOUTH UNIV
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