Method for synchronously removing antibiotic and heavy metal combined pollution in water

A technology for combined pollution and antibiotics, applied in water pollutants, chemical instruments and methods, water/sewage treatment, etc., can solve the problem of few effective ways to simultaneously remove combined pollution of antibiotics and heavy metals

Inactive Publication Date: 2020-10-20
SUZHOU UNIV OF SCI & TECH
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

At present, mesoporous carbon materials are mostly used in the removal of single antibiotics or heavy metal pollutan

Method used

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  • Method for synchronously removing antibiotic and heavy metal combined pollution in water
  • Method for synchronously removing antibiotic and heavy metal combined pollution in water
  • Method for synchronously removing antibiotic and heavy metal combined pollution in water

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0029] Preparation of glucose-based mesoporous carbon materials:

[0030] (1) Dissolve 1g of triblock copolymer F127 in 60mL of deionized water, then drop 11mL of hydrochloric acid and 5g of tetraethyl silicate into the F127 solution successively, stir, and conduct a hydrothermal reaction at 140°C for 24h, centrifuge after the reaction , washed, dried, and then roasted in an air tube furnace at 550°C to obtain white crystals;

[0031] (2) Dissolve 1 g of white crystals and 1.5 g of glucose in deionized water, and drop 80 μL of concentrated H 2 SO 4 (98%), reacted at 105°C for 7h and then reacted at 155°C for 7h, cooled, ground, and sieved to obtain a brown powder after the reaction was completed, and then the brown powder was placed in a nitrogen tube furnace to roast to obtain a black powder;

[0032] (3) adding the black powder into NaOH solution to remove the silicon template, drying and grinding to obtain the glucose-based mesoporous carbon material.

[0033] According ...

Embodiment 2

[0037] Glucose-based mesoporous carbon materials were prepared by the same method as in Example 1.

[0038] 5 groups of simulated water distributions B1 to B6 were prepared with laboratory deionized water. The simulated water distribution B1 of each group contained TC and Pb(II), the concentration of TC was 15mg / L, and the concentration of Pb(II) was 5 and 10 respectively. , 15, 20 and 30mg / L; each group of simulated water distribution B2 contains CIP and Pb(II), the concentration of CIP is 15mg / L, and the concentration of Pb(II) is 5, 10, 15, 20 and 30mg respectively / L; each group of simulated distribution water B3 contains SDZ and Pb(II), the concentration of SDZ is 15mg / L, and the concentration of Pb(II) is 5, 10, 15, 20 and 30mg / L; The distribution water B4 contains TC and Cu(II), the concentration of TC is 15 mg / L, and the concentration of Cu(II) is 5, 10, 15, 20 and 30 mg / L respectively; the simulated distribution water B5 of each group contains CIP and Cu(II), the con...

Embodiment 3

[0041] Glucose-based mesoporous carbon materials were prepared by the same method as in Example 1.

[0042] 5 groups of simulated distribution water C1~C6 were prepared with laboratory deionized water. The simulated distribution water C1 of each group contained TC and Pb(II), the concentration of Pb(II) was 10mg / L, and the concentration of TC was 5 and 10 respectively. , 15, 20 and 40mg / L; each group of simulated distribution water C2 contains CIP and Pb(II), the concentration of Pb(II) is 10mg / L, and the concentration of CIP is 5, 10, 15, 20 and 30mg respectively / L; each group of simulated distribution water C3 contains SDZ and Pb(II), the concentration of Pb(II) is 10mg / L, and the concentration of SDZ is 5, 10, 15, 20 and 30mg / L; The distribution water C4 contains TC and Cu(II), the concentration of Cu(II) is 10 mg / L, and the concentration of TC is 5, 10, 15, 20 and 40 mg / L respectively; the simulated distribution water C5 of each group contains CIP and Cu(II), the concent...

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Abstract

The invention discloses a method for synchronously removing antibiotic and heavy metal combined pollution in water, and belongs to the technical field of sewage treatment. The method comprises the following steps: adding a glucose-based mesoporous carbon material into a water body containing antibiotics and heavy metals, adjusting the pH value of the solution to 3-7, and carrying out an oscillation reaction at 22-28 DEG C for 180 min, wherein the addition amount of the glucose-based mesoporous carbon material is 0.5 g/L. The method is simple and convenient to operate and mild in condition, andcan realize synchronous and efficient removal of antibiotic and heavy metal combined pollution in the water body.

Description

technical field [0001] The invention relates to a method for synchronously removing combined pollution of antibiotics and heavy metals in water, belonging to the technical field of sewage treatment. Background technique [0002] At present, with the rapid development of livestock and poultry breeding, aquaculture and other industries, antibiotics or heavy metals are frequently detected in the water environment, posing an increasingly serious potential threat to the aquatic ecological environment and human health. The coexistence of antibiotics and heavy metals to form complex pollution has become one of the typical pollution types in the water environment and water treatment process. Due to the complexity of the coexistence characteristics of pollutants, the development of removal technologies for antibiotics and heavy metal complex pollutants has become a research hotspot and difficulty in the field of environment. In the comprehensive analysis of the adsorption and remova...

Claims

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Application Information

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IPC IPC(8): C02F1/28B01J20/20C02F101/20C02F101/30C02F101/34C02F101/38
CPCC02F1/283B01J20/20C02F2101/20C02F2101/30C02F2101/38C02F2101/34C02F2101/40B01J2220/4812B01J2220/4806
Inventor 许晓毅王斌吴玮吕晓辉温妍唐慧
Owner SUZHOU UNIV OF SCI & TECH
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