Method for adsorbing antibiotics in water by using silver-ytterbium modified biochar
A biochar and antibiotic technology, applied in the fields of adsorption water/sewage treatment, chemical instruments and methods, water pollutants, etc., can solve the problems of complicated biofilm culture process, easy pollution of membrane surface, and high requirements for reaction conditions, etc. Treatment way, shorten the time required for adsorption, good adsorption effect
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Embodiment 1
[0033] The preparation method of silver ytterbium modified biochar is:
[0034] (1) Wash the fungus residue, bake it at 70°C for 12 hours, and then crush it through a 60-mesh sieve to obtain the fungus residue powder;
[0035] (2) Evenly mix the powder of fungus residue and 1.5mol / L NaOH at a solid-to-liquid ratio of 1:4, soak for 4 hours, then dry at 80°C for 12 hours, then place in a tube furnace, and heat at 10°C in a nitrogen atmosphere Heating at a rate of 1 / min to 850°C for 3 hours, cooling to room temperature under the protection of nitrogen after the reaction, obtaining a carbonized product and grinding it into powder with a mortar;
[0036] (3) Wash the carbonized product with 1mol / L HCl solution to neutrality, then alternately rinse with distilled water and absolute ethanol for 3 times, then dry at 80°C for 6 hours to obtain A; dissolve A, silver nitrate and ytterbium nitrate in 50mL In deionized water, set the shaker temperature to 25°C, shake at 120r / min for 1h, t...
Embodiment 2
[0040] The influence of embodiment 2 adsorption time:
[0041] Add 500mL ciprofloxacin waste water in the 500mL conical flask, its mass concentration is 20mg / L, then add the silver ytterbium modified biochar of 0.1g embodiment 1 in the conical flask, at 25 ℃, with plastic wrap After sealing, place it on a rotary oscillator to vibrate at a speed of 120r / min, and use a needle tube at 1, 3, 5, 10, 15, 20, 25, 30, 60, 90, 120, 180, 240, 300, and 360 min Samples were taken and filtered through a 0.22 μm filter membrane to obtain water samples. The concentration of ciprofloxacin in the water samples was measured using a UV-visible spectrophotometer. The experiment was repeated three times, and the data were recorded in figure 2 .
[0042] figure 2 is the effect of time on the adsorption capacity of silver-ytterbium-modified biochar. Depend on figure 2 It can be seen that the adsorption capacity of silver-ytterbium-modified biochar to ciprofloxacin first increased and then gra...
Embodiment 3
[0043] Embodiment 3 The influence of initial concentration of ciprofloxacin
[0044] Add 150mL of ciprofloxacin waste water to a 250mL Erlenmeyer flask, and its mass concentration is 20mg / L, 40mg / L, 60mg / L, 80mg / L, 100mg / L, 120mg / L, 140mg / L, 160mg / L , 180mg / L, 200mg / L, then add 0.02g of the silver-ytterbium modified biochar of Example 1 into the Erlenmeyer flask, seal it with a plastic wrap at 25°C and place it on a rotary shaker at a speed of 120r / min. Shake, take a sample with a needle tube at 12 hours, and filter through a 0.22 μm filter membrane to obtain a water sample. The concentration of ciprofloxacin in the water sample is measured by a UV-visible spectrophotometer. The experiment is repeated three times, and the data are recorded in image 3 .
[0045] image 3 is the effect of the initial concentration on the adsorption capacity of silver-ytterbium modified biochar, given by image 3 It can be seen that the adsorption capacity of silver-ytterbium-modified biochar...
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