High-performance composite stabilizer for mercury-contaminated soil and method for repairing mercury-contaminated soil
A composite stabilizer and mercury pollution technology, which is applied in the field of high-efficiency composite stabilizers and heavy metal-contaminated soil treatment agents, can solve the problems of low cost and achieve the effects of wide applicability, insensitive soil physical and chemical properties, and obvious synergistic effect
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Embodiment 1
[0048] The mercury-contaminated site soil left over from the relocation of a chemical factory in Hunan was taken. The average mercury content in the soil was 120mg / kg. The mercury concentration is 0.13mg / L.
[0049] (1) Crushing and sieving the mercury-contaminated soil to a particle size ≤ 1 cm to remove larger stones and other debris;
[0050] (2) Add an appropriate amount of water to the mercury-contaminated soil to keep the soil moist so that various reactions can be carried out better, and then add a good oxidant (4% potassium persulfate solution is added to 5% HCl solution, the volume ratio 1:10), control the molar ratio of active ingredients in potassium persulfate to mercury element in the soil to be not less than 2:1, stir evenly, and heat for 20 minutes (the temperature is controlled at 80 degrees Celsius), so that the organic mercury and monovalent mercury in the soil into divalent mercury;
[0051] (3) Add 5% sodium sulfide solution, the addition of sodium sulfid...
Embodiment 2
[0057] Get the same soil as in Example 1, and through the same crushing and screening process, add an appropriate amount of water to the mercury-contaminated soil to keep the soil moist, then add the configured oxidant (4% sodium persulfate solution to 5% In the HCl solution, the volume ratio is 1:10), and the molar ratio of the active ingredient in the sodium persulfate to the mercury element in the soil is controlled to be not less than 2:1, stirred evenly, heated for 20min (the temperature is controlled at 80 degrees Celsius), and the remaining steps are Same as Example 1, after curing for 3 days, leaching was carried out according to the "Leaving Toxicity of Solid Waste Leach Method Horizontal Oscillating Method" (HJ557-2009), and the concentration of mercury in the leach solution was 0.0005mg / L, which was higher than the value in Example 1. However, it can meet the mercury leaching concentration requirements in the "Soil Remediation Standards for Heavy Metal Contaminated S...
Embodiment 3
[0059] Get the same soil as in Example 1, and through the same crushing and screening process, add the same oxidizing agent as in Example 1 to carry out the same oxidation reaction, add 5% potassium sulfide solution, and the addition of potassium sulfide is equal to the sulfur element and the soil. The molar ratio of the mercury element in the medium is 2:1, stir evenly, react for 30 minutes, add ferrous chloride, the addition amount is 1% of the soil mass, stir evenly, react for 15 minutes; add bentonite, zeolite and humus The mass ratio is 1:1:1, the total addition is 5% of the soil mass, and it is evenly stirred; the next step of adjusting the pH is the same as in Example 1, and after 3 days of curing, follow the "Solid Waste Leaching Toxicity Leaching Method Horizontal Oscillation Method" (HJ557-2009) is leached, and the concentration of mercury in its leachate is 0.0008mg / L, is higher than the value in embodiment 1, but can meet the heavy metal pollution in " heavy metal c...
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