Mercury removal adsorbent with core-shell structure, and preparation method thereof
A technology of core-shell structure and adsorbent, which is applied in the field of mercury removal adsorbent with core-shell structure and its preparation, can solve the problem that nanomaterials remove typical toxic pollution without significant efficiency, and achieve controllable shape and size , easy preparation, good catalytic and adsorption performance
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Embodiment 1
[0030] This embodiment provides a method for preparing a mercury removal adsorbent with a core-shell structure, and the specific steps are as follows:
[0031] Step 1: Add 1.35gFeCl 3 ·6H 2 O is dissolved in 40mL pure ethylene glycol solution (concentration> 99%), use a magnetic stirrer to stir for 30 minutes, add 3.6g anhydrous sodium acetate, 1.0g polyethylene glycol, and magnetically stir for 60-90 minutes at a speed of 5r / min; transfer the resulting solution to a 100ml water reactor at 200°C After the reaction is completed for 8 hours, the reaction is completed, cooled to room temperature, and washed repeatedly with absolute ethanol and deionized water for 3 to 5 times, and the washed Fe 3 O 4 The nanoparticles are put into an oven and dried at a temperature of 60℃ to obtain clean Fe 3 O 4 Nanoparticle
[0032] Step 2: Add 1.75g of ammonium molybdate tetrahydrate [(NH4) 6 Mo 7 O 24 ·4H 2 O], 3.8g of thiourea was added to 50mL of deionized water, and stirred with a magnetic sti...
Embodiment 2
[0036] The difference between this embodiment and embodiment 1 is that the hydrothermal reaction temperature in step 4 is 180° C., and the remaining steps are the same as those in embodiment 1, and finally, mercury removal adsorbent 2 is obtained.
Embodiment 3
[0038] The difference between this embodiment and embodiment 1 is that the hydrothermal reaction temperature in step 4 is 200° C., and the remaining steps are the same as those in embodiment 1, and finally, mercury removal adsorbent 3 is obtained.
[0039] Such as figure 1 , 2 , 3 shows that as the synthesis temperature increases, Fe 3 O 4 Nanoparticles are coated with more MoS 2 Nanosheet, MoS 2 The crystallinity and degree of order of the nanosheets also increase.
[0040] Such as Figure 4 , 5 、6, for the simulated power plant flue gas (120℃) environment, and N 2 As a carrier gas, the mercury removal rate of mercury removal adsorbent 1 and mercury removal adsorbent 2 can almost reach 100% within 50 minutes, and the mercury removal rate of mercury removal adsorbent 3 is between 98%-100%, and they are all very stable. The mercury removal rate of molybdenum disulfide produced by the process generally only reaches about 80%, indicating that the mercury removal effect of the present ...
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