Preparation method of Cr(VI) adsorbent and application thereof in waste water treatment
A technology of adsorbent and ultrapure water, which is applied in the field of preparation of high-efficiency adsorbent for target toxic metal ion Cr, can solve the problems of small adsorption capacity and high price, and achieve the effect of simple preparation method, low cost and excellent adsorption performance
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Embodiment 1
[0022] The preparation method of the Cr(Ⅵ)-containing wastewater adsorbent is as follows:
[0023] Take 26.65 ml of concentrated sulfuric acid with a mass concentration of 98%, weigh 0.395 g of 1,8-naphthalene diamine (DAN) and 4.57 ml of aniline (AN), dissolve it in a 250 ml volumetric flask A, and dilute to volume with ultrapure water. Take 17.09 g of ammonium persulfate (APS) and dissolve it in ultrapure water, and put it in volumetric flask B of 250 ml. Transfer the solution from the two volumetric flasks into a beaker, and stir for 5 h under normal pressure at 5 °C. The resulting cloudy solution was filtered with a 0.22 μm filter membrane, washed with ultrapure water until it was colorless, and dried under vacuum at 60 °C for 12 h. , the obtained solid was ground to powder, and the high-efficiency Cr(Ⅵ) adsorbent was prepared with a yield of 37.61%.
Embodiment 2-3
[0025] The difference between Examples 2 and 3 and Example 1 is that different amounts of ammonium persulfate (APS) are used in the synthesis process of the high-efficiency Cr(VI) adsorbent, and the amounts of other raw materials and operating conditions are the same. The raw material ratio of embodiment 1-4 is shown in table 1.
[0026] Table 1
[0027] Example number n(APS):n(AN) Aniline (AN) amount / ml Amount of ammonium persulfate (APS) / g Amount of 1,8-naphthalene diamine (DAN) / g Yield / % 1 0.4:1 4.57 4.564 0.395 37.61 2 1.5:1 4.57 17.115 0.395 108.44 3 2.1:1 4.57 23.961 0.395 39.57
Embodiment 4
[0029] Influence of coexisting ions on adsorption effect
[0030] K + , Ca 2+ , SO 4 2- 、HCO 3 - , Cl - Plasma is a common ion in natural water bodies and industrial wastewater, and they can compete with toxic metal ions in water for active sites on the adsorbent. In a 10ml stoppered polypropylene tube, add 5mg of the obtained Cr(VI) adsorbent and 10ml of Cr(VI)-containing wastewater containing different concentrations of coexisting ions (the initial concentration of Cr(VI) is 10 mg / L, and the coexisting ions are K + , Ca 2+ , SO 4 2- 、HCO 3 - , Cl - , the concentration range is 2.5-30 mmol / L). Mix the solution in the tube evenly, fix it in a digital display constant temperature shaking incubator at 25.0±1.0°C and shake it at a speed of 150 r / min, take it out after 24 hours and quickly filter it with a cellulose acetate filter membrane with a pore size of 0.22 μm. The concentration of Cr(VI) in the filtrate was determined by flame atomic absorption spectrome...
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Abstract
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