Preparation method of cerium-loaded material of hydrochloric acid modified zeolite and application in norfloxacin-polluted water body
A technology for modifying zeolite and zeolite, which is used in water pollutants, water/sewage treatment, chemical instruments and methods, etc., can solve the problems of long reaction time and low adsorption rate of norfloxacin, and achieves low cost and effective space. The effect of widening and high adsorption rate
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Embodiment 1
[0036] The preparation method of modified zeolite, comprises the steps:
[0037] 1) Pass natural clinoptilolite through 8-mesh and 20-mesh standard sieves, take zeolite between 8-mesh and 20-mesh, shake and wash with deionized water several times, soak in deionized water for 12 hours, and dry at 105°C.
[0038] 2) Nitric acid, sodium hydroxide, and sodium chloride solutions with concentrations of 0.2mol / L, 0.5mol / L, and 1.0mol / L were prepared respectively, and the prepared concentrations were 0.05mol / L, 0.1mol / L, 0.2mol / L, Take 100 mL of 0.5 mol / L and 1.0 mol / L hydrochloric acid solutions into conical flasks respectively, and add 10 g of zeolite after particle size pretreatment respectively. Oscillate for 2h in a constant temperature oscillator with a rotational speed of 200r / min.
[0039] 3) The reacted zeolite is taken out, washed with deionized water until neutral, and dried at 105°C.
[0040] The scanning electron microscope pictures of natural zeolite and material G are...
Embodiment 2
[0042]The preparation method of modified zeolite, comprises the steps:
[0043] Take 10g of material G, and take 1.86g of cerium chloride heptahydrate into a beaker, add 100mL of deionized water, and heat in a water bath at 70°C for 3h. Evaporate to dryness in a water bath at 100°C, and dry at 50°C.
[0044] The EDS spectra of natural zeolite, material G and material Ce@G zeolite are as follows image 3 As shown, compared with the mass percentage of natural zeolite aluminum in material G, the thermal stability and hydrothermal stability of material G are enhanced. Compared with natural zeolite and material G, Ce@G zeolite has a new Ce in the spectrum. while in figure 1 In the scanning electron microscope analysis of the material, a white substance appeared on the surface of the material Ce@G zeolite. Combining these two characterizations, it can be proved that Ce is loaded on the surface of material G.
Embodiment 3
[0046] The effect of zeolite on the loading rate of cerium on the adsorption kinetics of norfloxacin:
[0047] 1) Take 10g of material G, respectively take 3.73g, 1.86g, 0.93g, 0.47g, and 0.23g of cerium chloride heptahydrate into a beaker, add 100mL of deionized water, and heat in a water bath at 70°C for 3h. Evaporate to dryness in a water bath at 100°C, and dry at 50°C. Materials A, Ce@G zeolite, C, D, E were obtained.
[0048] 2) Pipette 100mL of norfloxacin solution with a concentration of 10mg / L into a conical flask, place it in a constant temperature oscillator, and add 1g of materials A, Ce@G zeolite, C, and D to each conical flask respectively With E, the oscillation temperature is 298K, and the oscillation speed is 200r / min. The supernatant was taken at 5min, 15min, 30min, 45min, 60min, 90min, 120min, 180min, 240min and 300min respectively, passed through a 0.22μm filter membrane, and determined in HPLC. Two parallel samples were set up for each reaction.
[0049...
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