Amino functionalized hydrophobic zeolite, preparation method and applications thereof
An amino-functionalized, hydrophobic technology, applied in chemical instruments and methods, water pollutants, other chemical processes, etc., can solve the problem of low adsorption and achieve the effect of strong hydrophobicity
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[0033] The amino functionalized hydrophobic zeolite prepared by the preparation method of the present invention has a pH of 2, an adsorbent dosage of 4.0g / L, Cr 2 o 7 2- Under the condition of ion concentration of 50mg / L and adsorption time of 1h, the Cr 2 o 7 2- The removal rate of ions can reach 84.2-96.4%. The adsorption capacity of water vapor is 22.8-31.0 mg / g under the condition of relative humidity of 75%.
[0034] Under the conditions of pH 5, adsorbent dosage 4.0g / L, phenol concentration 50mg / L, and adsorption time 1h, the removal rate of phenol can reach 75.9-89.1%.
Embodiment 1
[0037] The preparation method of the amino-functionalized hydrophobic zeolite of the present embodiment is carried out according to the following steps:
[0038] First add 5g of natural clinoptilolite into 100mL of 3-aminopropyltrimethoxysilane solution with cyclohexane as the solvent concentration of 15g / L and react at 25°C for 24h, then filter with suction, wash with absolute ethanol, Drying makes amino-functionalized hydrophobic zeolite (the XRD pattern of samples is as follows figure 1 As shown, the TG / TDG curve is as image 3 shown).
[0039] Configuration 50mg / LCr 2 o 7 2- ions, adjust the pH of the solution to 2, add 0.2g amino-functionalized hydrophobic zeolite sample to 50mLCr 2 o 7 2- The ionic solution was stirred for 1 h with a magnetic stirrer. The supernatant of the treated solution was taken, centrifuged, and then filtered through 0.45 μm filter paper. Evaluation of Cr by UV-Vis Spectrophotometer 2 o 7 2- The removal effect of , the calculation formu...
Embodiment 2~19
[0042] Embodiment 2~19, method is with embodiment 1, the condition of each embodiment, Cr 2 o 7 2- The ion removal rate, water vapor adsorption capacity and phenol removal rate are shown in Table 1.
[0043] Table 1
[0044]
[0045]
[0046] In conjunction with the above examples, it can be drawn that after the natural clinoptilolite is modified by using an aminosilane coupling agent, its effect on Cr 2 o 7 2- The removal rate of ions is significantly improved, the adsorption capacity of water vapor is significantly reduced, and the removal rate of phenol is significantly increased. Cr 2 o 7 2- The removal rates of ions and phenol were increased; while the water vapor adsorption of the modified sample decreased with the increase of aminosilane coupling agent concentration, then increased slightly, and then tended to be flat, which was mainly due to the aminosilane coupling agent concentration increased. It is caused by the combined action of the hydrophilic ami...
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