Method for efficient remediation of mercury-contaminated soil by leaching and leaching agent
A mercury pollution and leaching technology, applied in the restoration of polluted soil, etc., can solve the problems of low secondary pollution, low leaching efficiency, low mercury residue, etc., achieve good effect, enhance leaching efficiency, synergistic powerful effect
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Embodiment 1
[0046] The contaminated farmland soil around a mercury mine in Guizhou was taken, and the mercury content in the soil was 7.8 mg / kg. After the soil was naturally air-dried, it was ground and passed through a 20-mesh sieve for use. Configure oxidizing agent, eluent I and eluent II respectively, wherein oxidant is that 4% potassium persulfate solution is added in 5% HCl solution, the volume ratio is 1:10, and the concentration of citric acid in eluent I is 1moL / L, the concentration of potassium iodide is 0.1moL / L, the concentration of calcium chloride is 0.3moL / L, the mass percentage concentration of sodium sulfide in the eluent II is 5%, and the amount of sodium hydroxide added is 1.5% of the amount of sodium sulfide. Weigh 5g of the pretreated soil into a 100mL centrifuge tube, add deionized water to keep the soil moist, and then add the prepared oxidant potassium persulfate solution to control the potassium persulfate in the potassium persulfate solution and the mercury in the...
Embodiment 2
[0053] Get the same soil as in Example 1, and through the same air-drying, grinding and sieving process, configure oxidizing agent, eluent I and eluent II respectively, wherein the oxidizing agent is that 4% sodium persulfate solution is added to 5% In the HCl solution, the volume ratio is 1:10, and the eluent I is citric acid, sodium iodide and sodium chloride, wherein the concentration of citric acid is 1moL / L, the concentration of sodium iodide is 0.1moL / L, and the concentration of sodium chloride is 0.1moL / L. Concentration is 0.3moL / L, and eluent II is identical with embodiment 1. Take by weighing 5g of pretreated soil in a 100mL centrifuge tube, the next oxidation step is the same as in Example 1, and the mercury content in the soil measured after air-drying is 0.87mg / kg, which is higher than the value in Example 1 , but lower than the "Soil Environmental Quality Standard" (GB15618-1995) level 3 standard value (1.5mg / kg), the soil mercury removal rate is 88.85%.
Embodiment 3
[0055] Get the same soil as in Example 1, and through the same air-drying, grinding and sieving process, configure oxidizing agent, eluent I and eluent II respectively, wherein the oxidizing agent is that 4% potassium persulfate solution is added to 5% In the HCl solution, the volume ratio is 1:10, and the eluent I is tartaric acid, potassium iodide and potassium chloride, wherein the concentration of tartaric acid is 1moL / L, the concentration of potassium iodide is 0.1moL / L, and the concentration of potassium chloride is 0.3moL / L , Eluent II is the same as in Example 1. Take by weighing 5g of pretreated soil in a 100mL centrifuge tube, the next oxidation step is the same as in Example 1, and the mercury content in the soil measured after air-drying is 0.81 mg / kg, which is higher than the value in Example 1 , but lower than the "Soil Environmental Quality Standard" (GB15618-1995) level 3 standard value (1.5mg / kg), the soil mercury removal rate is 89.62%.
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