A method for efficient stabilization of mercury-containing waste residue
A stabilization and waste residue technology, applied to the removal of solid waste, etc., can solve the problems of not necessarily stabilizing mercury-containing waste residues, weakening bioavailability, and reducing mercury mobility, so as to achieve insensitive waste residue properties and improve the stabilization effect , Reduce the effect of migration and bioavailability
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Embodiment 1
[0051] The waste slag left over from the smelting of a mercury mine in Tongren, Guizhou was taken. The mercury content in the waste slag was as high as 1150mg / kg. The slag sample was leached according to the "Solid Waste Leaching Toxic Leaching Method Sulfuric Acid Nitric Acid Method" (HJ / T299-2007). The concentration of mercury is 3.25mg / L, which exceeds the concentration limit of 0.1mg / L in the "Identification Standard for Hazardous Waste Leach Toxicity" (GB5085.3-2007), and this mercury-containing waste residue is hazardous waste. The slag sample was leached according to the Horizontal Oscillating Method of Toxic Leaching Method for Solid Waste Leaching (HJ557-2009), and the concentration of mercury in the leaching solution was 1.68mg / L, which exceeded the "Hazardous Waste Landfill Pollution Control Standard" (GB18598- 2001), the concentration limit allowed to enter the landfill is 0.25mg / L, and it needs to be stabilized and solidified to meet the entry standard.
[0052] (...
Embodiment 2
[0060] Get the same waste slag as in Example 1, and through the same crushing and screening process, add an appropriate amount of water in the waste slag to keep the waste slag moist, then add the configured oxidant (4% sodium persulfate solution into 5% HCl solution , the volume ratio is 1:10), the molar ratio of the active ingredient in the sodium persulfate to the mercury element in the waste residue is controlled to be not less than 2:1, stir evenly, heat for 20min (the temperature is controlled at 80 degrees Celsius), and the rest of the steps are carried out Example 1 is the same, after curing for 3 days, leaching is carried out according to "Solid Waste Leaching Toxicity Leaching Method Horizontal Oscillation Method" (HJ557-2009), the concentration of mercury in its leach solution is 0.13mg / L, which is higher than the value in Example 1, but can It meets the concentration limit of 0.25mg / L allowed to enter the landfill in the "Hazardous Waste Landfill Pollution Control S...
Embodiment 3
[0062] Get the same waste residue as in Example 1, and through the same crushing and screening process, add the same oxidizing agent as in Example 1 and carry out the same oxidation reaction, add 5% potassium sulfide solution, and the addition of potassium sulfide is the amount of sulfur element and waste residue 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 2% of the waste residue mass, stir evenly, react for 15 minutes; add bentonite, zeolite and humus The mass ratio is 1:1:1, the total addition is 10% of the waste slag quality, and it is evenly stirred; the next step of adjusting the pH is the same as in Example 1, and after 3 days of maintenance, follow the "Solid Waste Leaching Toxicity Leaching Method Horizontal Oscillation Method" (HJ557-2009) is leached, and the concentration of mercury in its leachate is 0.15mg / L, higher than the value in embodiment 1, but can satisfy " hazar...
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