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Activated carbon for efficiently treating chromium wastewater, and preparation method and application thereof

A technology of activated carbon and modification, which is applied in water/sewage treatment, chemical instruments and methods, adsorption water/sewage treatment, etc., can solve the problem of reduced chromium adsorption capacity, achieve wide pH universality, wide range of sources, and solve wastewater The effect of pH limitation

Pending Publication Date: 2022-01-14
ZHEJIANG HUADONG ENG CONSTR MANAGEMENT +1
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

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Problems solved by technology

[0005] In addition, studies have shown that activated carbon has salt ions, such as Na + , Ca 2+ The adsorption capacity of chromium will be greatly reduced in the presence of such salt ions (Wei Jun. Research on the adsorption of heavy metals on biochar-loaded hydroxyapatite composite materials [D]. Anhui: Anqing Normal University, Anhui.), but these salt ions are present in wastewater inevitable

Method used

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  • Activated carbon for efficiently treating chromium wastewater, and preparation method and application thereof
  • Activated carbon for efficiently treating chromium wastewater, and preparation method and application thereof
  • Activated carbon for efficiently treating chromium wastewater, and preparation method and application thereof

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0037] Activation with 30 g / L of NaOH, the mass fraction of modified humic acid is 2 g / L, including the following steps:

[0038] S1, harvesting Ophiopogon japonicus at 105 o Dry at C for 24 h;

[0039] S2, placing the dried Ophiopogon japonicus in 30 g / L KOH for activation for 24 h;

[0040] S3, the activated Ophiopogon japonicus is taken out at 105 o Dry at C for 24 h;

[0041] S4, the dried Ophiopogon japonicus is placed in the muffle furnace with 8 o The heating rate of C / min is raised to 700 o C for carbonization and keep for 1 h;

[0042] S5. After natural cooling at room temperature, pickle with 0.1 mol / L hydrochloric acid, then wash with distilled water until the filtrate is neutral, filter the activated carbon and dry it at 105 o C to dry.

[0043] S6, modifying the prepared activated carbon with humic acid,

[0044] The specific steps are: add the dried activated carbon to 1% NaOH solution containing humic acid (mass fraction 2 g / L) and soak for 24 h. The mas...

Embodiment 2

[0047] Activation with 76 g / L of NaOH, the mass fraction of modified humic acid is 2 g / L, including the following steps:

[0048] S1, harvesting Ophiopogon japonicus at 105 o Dry at C for 24 h;

[0049] S2, placing the dried Ophiopogon japonicus in 76 g / L KOH for activation for 24 h;

[0050] S3, the activated Ophiopogon japonicus is taken out at 105 o Dry at C for 24 h;

[0051] S4, the dried Ophiopogon japonicus is placed in the muffle furnace with 10 o The heating rate of C / min is raised to 800 o C for carbonization and keep for 1 h;

[0052] S5, after natural cooling at room temperature, pickle with 0.1 mol / L hydrochloric acid, then wash with distilled water until the filtrate is neutral, filter the activated carbon and remove it at 105 o C to dry.

[0053] S6. Modify the prepared activated carbon with humic acid. The specific steps are: add the dried activated carbon to a 1% NaOH solution containing humic acid (mass fraction 2 g / L) and soak for 24 h. The mass rati...

Embodiment 3

[0055] Adsorption performance test of hexavalent chromium

[0056]Disperse 0.06 g of the product obtained in Example 1 in 200 mL of deionized water, mix and stir evenly, then add 0.056 g of potassium dichromate (Cr(VI) concentration is 100 mg / L), pH=1 ~ 5, stirred for 24 h, filtered to obtain the supernatant, measured the remaining content of chromate with an inductively coupled plasma spectrometer (ICP), and calculated the amount of chromate adsorbed by the adsorbent through conversion. The amount is 315 mg / g.

[0057] figure 2 For the isotherm of the activated carbon material prepared by the present invention to adsorb Cr(VI), the abscissa is the adsorption equilibrium concentration, and the ordinate is the adsorption amount. It can be seen from the figure that its maximum adsorption amount can reach 315 mg / g.

[0058] image 3 For the modified activated carbon prepared by the present invention, when there is or is not 100 mg / LCa (II) ion, to Cr (VI) adsorption situation...

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Abstract

The invention belongs to the technical field of water treatment, and particularly relates to activated carbon for efficiently treating chromium wastewater, and a preparation method and application thereof. The preparation method comprises the following steps: S1, cutting ophiopogon japonicus and drying at the temperature of 30-105 DEG C; S2, placing the dried ophiopogon japonicus in KOH, and soaking and activating; S3, taking out the activated ophiopogon japonicus, and drying at the temperature of 105 DEG C; S4, placing the dried ophiopogon japonicus in a muffle furnace for carbonization; S5, after carbonization, naturally cooling at room temperature, pickling with hydrochloric acid, washing with distilled water until filtrate is neutral, filtering, and drying at the temperature of 105 DEG C; and S6, modifying the prepared activated carbon with humic acid. The ophiopogon japonicus is used as a preparation raw material of the activated carbon, the ophiopogon japonicus is rapid in growth and propagation, wide in source and low in price, and the prepared activated carbon is rich in pores and large in specific surface area after being modified by humic acid, and particularly has high selectivity on Cr<6+>.

Description

technical field [0001] The invention belongs to the technical field of water treatment, and in particular relates to an activated carbon for efficiently treating chromium wastewater, a preparation method and an application thereof. Background technique [0002] A large amount of chromium-containing wastewater produced in industrial mining, mineral processing, smelting and other processes is the main source of chromium pollutants, which will also cause water and soil pollution. Chromium is extremely harmful to the human body, and the toxicity of hexavalent chromium is far greater than that of trivalent chromium (Sidney, A, Katz, et al. The toxicity of chromium with respect to its chemical specification: A review[J]. Journal of Applied Toxicology , 1993, 13(3):217-224.). [0003] At present, the methods used to deal with chromium mainly include adsorption method, precipitation method, redox method and ion exchange method, and the most used method is adsorption method. [000...

Claims

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Application Information

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IPC IPC(8): C01B32/348C01B32/318C01B32/354B01J20/20B01J20/30C02F1/28C02F101/22
CPCC01B32/348C01B32/318C01B32/354B01J20/20C02F1/283C02F2101/22
Inventor 陆泓波任金明王永明丁聪吴坚李瑞泽秦亚光刘万鹏高远
Owner ZHEJIANG HUADONG ENG CONSTR MANAGEMENT