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Immobilized combination agent and method for immobilizing As (III) and heavy metal-containing waste residues by using immobilized combination agent

A combination agent and immobilization technology, which is applied to the protection device against harmful chemical agents, etc., can solve the problems of lack of research on screening and combination technology system, high ratio of cement addition and volume increase, and different arsenic fixation effects. The effect of reducing the risk of toxic leaching, alleviating the pressure on stockpiles and landfills, and rationally utilizing resources

Pending Publication Date: 2022-07-01
有研资源环境技术研究院(北京)有限公司 +1
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0006] The traditional curing and stabilizing agents mainly use cement and lime as the main body, but the addition of too much cement will easily lead to an excessively high volumetric ratio, and the strong alkaline environment is not conducive to the fixation of arsenic. As(V) and As(III ) anion exists in the waste residue, most of the immobilization materials are only effective for As(V), but it is difficult to form a stable compound with As(III), often ineffective for As(III), and are effective for cationic heavy metals such as lead and cadmium. Most materials with immobilization effects are ineffective for arsenic, and different iron salts have different arsenic fixation effects. The research on the screening and combination technology system of various materials with long-term immobilization effects on arsenic and heavy metals is still relatively lacking.

Method used

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Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0034] The oxidant is analytically pure potassium permanganate (KMnO 4 ).

[0035] The mass ratio of ferrous sulfate heptahydrate, ferric chloride, and sodium sulfide nonahydrate is ferrous sulfate heptahydrate: ferric chloride: sodium sulfide nonahydrate=4:1:4, which is combined into the waste residue containing high concentrations of heavy metals. The addition ratio is 2 wt %, wherein the sodium sulfide nonahydrate is first dissolved in water whose added mass is 20 wt % of the quality of the waste residue.

[0036] Preparation of other stabilizers: mix sodium-based bentonite, calcium carbide sludge, light-burned magnesia, and phosphate rock powder in a mass ratio of 1:4:4:1, and pass through a 200-mesh sieve. Among them, calcium carbide sludge in the combination agent is taken from Hunan A waste slag field contains about 39% calcium hydroxide and 50% moisture content.

[0037] The curing agent adopts commercially available PC325# cement.

[0038] Commercially available an...

Embodiment 2

[0048] The oxidant is analytically pure potassium permanganate (KMnO 4 ), the mass percentage added to the waste residue is 2wt%.

[0049] The mass ratio of ferrous sulfate heptahydrate, ferric chloride, and sodium sulfide nonahydrate is ferrous sulfate heptahydrate: ferric chloride: sodium sulfide nonahydrate = 1:4:1. The combined dosage ratio in the waste residue is 2wt%, wherein the sodium sulfide nonahydrate is first dissolved in water with an added quality of 20wt% of the waste residue.

[0050] Preparation of other stabilizers: mix sodium-based bentonite, calcium carbide sludge, light-burned magnesia, and phosphate rock powder in a mass ratio of 1:2:4:1, and pass through a 200-mesh sieve, wherein the moisture content of calcium carbide sludge in the composition is 45%, about 37% calcium hydroxide.

[0051] The curing agent adopts commercially available PO425# cement.

[0052] The pH regulator used calcium carbonate.

[0053] The wastewater treatment of a smelting aci...

Embodiment 3

[0061] The oxidant is analytically pure potassium permanganate (KMnO 4 ).

[0062] The mass ratio of ferrous sulfate heptahydrate, ferric chloride, and sodium sulfide nonahydrate is ferrous sulfate heptahydrate: ferric chloride: sodium sulfide nonahydrate=4:1:4, which is combined into the waste residue containing high concentrations of heavy metals. The addition ratio is 2wt%, wherein the sodium sulfide nonahydrate is first dissolved in water with an added quality of 20wt% of the waste residue.

[0063] Preparation of other stabilizers: mix sodium-based bentonite, calcium carbide sludge, light-burned magnesia, and phosphate rock powder in a mass ratio of 1:2:4:1, and pass through a 200-mesh sieve, wherein the moisture content of calcium carbide sludge in the composition is 50%, about 40% calcium hydroxide.

[0064] The curing agent adopts commercially available PC325# cement.

[0065] The pH regulator used commercially available analytically pure phosphoric acid.

[0066] ...

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Abstract

The invention provides an immobilized combination agent and a method for immobilizing As (III) and heavy metal-containing waste residues by using the same. The immobilized combination agent comprises an oxidizing agent, a stabilizing agent, a curing agent and a pH value regulator, and the stabilizing agent is composed of ferric salt, ferrous salt, sulfide, sodium bentonite, light calcined magnesia, rock phosphate powder and calcium carbide sludge. The immobilization method comprises the following steps: crushing and screening original waste residues, and fully mixing and stirring with an oxidizing agent to obtain primary waste residues; adding ferrous salt or ferric salt and sulfide aqueous solution into the first-stage waste residue, and uniformly stirring and mixing to obtain second-stage waste residue; sodium bentonite, calcium carbide sludge, light calcined magnesia, rock phosphate powder and water are added into the second-stage waste residues, and third-stage waste residues are obtained; and adding a curing agent and water into the third-stage waste residue, forcibly stirring, discharging and curing. By means of the method, high-content arsenic and heavy metal (cadmium, lead, copper, zinc, chromium, mercury and the like) in the waste residues can be efficiently fixed, the toxic leaching concentration of the arsenic and the heavy metal is obviously reduced, and the requirement for safe disposal is met.

Description

technical field [0001] The invention belongs to the field of comprehensive treatment of heavy metal pollution, and particularly relates to an immobilization composition suitable for As(III) and heavy metal waste residues and a method for immobilizing the immobilization composition to treat waste residues containing high concentrations of heavy metals. Background technique [0002] With the continuous development of the chemical industry, non-ferrous metal mining, smelting industry and electronics industry, the hazardous waste residues of heavy metals enter the environment and become an important source of pollution. Under the action of erosion and soil erosion, it will cause serious environmental risks to soil and water bodies, and directly threaten the health of the population. At present, the commonly used treatment methods mainly include physical and chemical remediation and bioremediation methods, such as landfill method, leaching (washing) method, foreign soil method, l...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): A62D3/33A62D101/43
CPCA62D3/33A62D2101/43A62D2203/02
Inventor 于冰冰袁学韬陈勃伟刘兴宇张明江王建雷徐政刘美林高博文
Owner 有研资源环境技术研究院(北京)有限公司
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