A method of low-temperature thermal desorption combined with chemical leaching to remediate mercury-contaminated soil
A technology of chemical leaching and mercury pollution, applied in the restoration of polluted soil, etc., can solve the problems of low efficiency of leaching and restoration, high energy consumption of heat treatment, and small soil damage, so as to reduce soil structure damage and improve leaching. Efficiency, effective treatment effect
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Embodiment 1
[0044] Take the soil from the mercury contaminated site left by the relocation of a chemical plant in Hunan. The average mercury content in the soil is 120mg / kg. The soil is dried and crushed for use. Prepare each eluent separately. The mixed solution containing organic acid, iodide salt and chloride salt contains citric acid concentration of 1moL / L, potassium iodide concentration of 0.1moL / L, calcium chloride concentration of 0.3moL / L, and sulfide salt The mass percentage concentration of sodium sulfide in the sodium hydroxide solution is 5%, and the amount of sodium hydroxide added is 1.5% of the amount of sodium sulfide. Weigh 500g of the pretreated soil and put it into a heat treatment device for heat treatment, set a treatment temperature of 350°C, and a treatment time of 30 minutes. The heat-treated soil is unearthed from the discharge port, the mercury in the tail gas is condensed and recovered, and then the residual mercury is removed by activated carbon adsorption. Aft...
Embodiment 2
[0052] Take the same soil as in Example 1, and undergo the same air-drying and crushing treatments, and configure the same leaching solutions as in Example 1. Weigh 500g of the pretreated soil and put it into a heat treatment device, and heat treatment under the conditions of a treatment temperature of 350°C and a treatment time of 20, 30, and 40 minutes. The heat-treated soil was cooled to room temperature and subjected to the same leaching treatment as in Example 1. After air-drying, the soil mercury content was determined to be 2.13mg / kg, 1.15mg / kg, 1.01mg / kg, and the removal rates of mercury in the soil were respectively It is 98.23%, 99.04%, 99.16%. When the treatment time was 30 and 40 minutes, the mercury content in the soil was lower than the third-level standard value (1.5mg / kg) of "Soil Environmental Quality Standard" (GB15618-1995).
Embodiment 3
[0054] Take the same soil as in Example 1, and undergo the same air-drying and crushing treatments, and configure the same leaching solutions as in Example 1. Weigh 500g of the pretreated soil and put it into the heat treatment device, and heat treatment under the conditions of setting treatment time of 30 minutes and treatment temperature of 250, 300, and 350°C. The heat-treated soil was cooled to room temperature and subjected to the same leaching treatment as in Example 1. After air-drying, the soil mercury content was determined to be 1.96mg / kg, 1.05mg / kg, 0.94mg / kg, and the removal rates of mercury in the soil were respectively It is 98.37%, 99.13%, 99.27%. The mercury content in the soil was lower than the third-level standard value (1.5mg / kg) of "Soil Environmental Quality Standard" (GB15618-1995) when the treatment temperature was 300 and 350 ℃ respectively.
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