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Iron-silver co-doped biochar with high adsorption capacity and preparation method of iron-silver co-doped biochar

A technology of co-doping and high adsorption, applied in the fields of biofuels, chemical instruments and methods, adsorbed water/sewage treatment, etc., can solve the problems of uneven load, large consumption of chemical reagents, uneven materials, etc. Resource utilization, low consumption of chemical reagents and small amount of iron leaching

Active Publication Date: 2022-06-07
GUILIN UNIVERSITY OF TECHNOLOGY
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  • Abstract
  • Description
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AI Technical Summary

Problems solved by technology

However, due to certain defects in the preparation technology, the biochar and the loaded metals are easy to leach, causing secondary pollution of the water body.
[0003] At present, there are not many reports about the simultaneous loading of iron and silver on biochar. The preparation methods are mainly liquid phase reduction method and gel method. For example, the gel method adopted in Chinese patent application CN108115152A first introduces lithium magnesium silicate and polygu A mixed solution containing iron and silver was prepared with amino acid, and a dry gel was formed by heating for a long time, and finally heated at high temperature again to obtain magnetic biochar loaded with iron and silver; however, the preparation process of this method is complicated, and more impurity elements and Chemical agent, heating for many times for a long time consumes a lot of energy, and the economic benefit is low
Another example is the method published by Chinese patent application CN106955667A which adopts the liquid phase reduction method to prepare activated carbon-loaded nano-iron and silver clusters. Although the loading of silver makes the material have certain catalytic properties, the silver metal clusters cause the inhomogeneity of the material. The preparation process Silver ions are easy to form precipitates, which makes the loading efficiency low, and the preparation steps are complicated, the consumption of chemical reagents is large, and the economical practicability is poor.
[0004] At present, the methods for loading metals on biochar mainly include co-precipitation method, co-pyrolysis method, and liquid phase reduction method. The binding ability of the iron-silver co-doped biochar with low risk of metal leaching and high adsorption capacity and its preparation method are lacking.

Method used

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  • Iron-silver co-doped biochar with high adsorption capacity and preparation method of iron-silver co-doped biochar
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  • Iron-silver co-doped biochar with high adsorption capacity and preparation method of iron-silver co-doped biochar

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0036] Example 1. Preparation of iron-silver co-doped biochar (FSHC) and iron-doped biochar (FHC)

[0037] 1. Preparation method of FSHC

[0038] After drying the Li Shihe plant body to constant weight to obtain Li Shihe biomass, then co-doping with iron and silver, operate according to the following steps:

[0039] (1) Take 50 mL of ultrapure water to prepare a mixed solution system: under stirring conditions, add 3 mL of concentrated H into the beaker in turn 3 PO4 (concentration 85wt%), 3gFe (NO 3 ) 3 ·9H 2 O, 0.3g AgNO 3 , placed in an ultrasonic cleaner for 10min to disperse the solution uniformly;

[0040] (2) get 3g dried to constant weight of Li's wort biomass (that is, the sample obtained after Li's wort plant body is dried), pulverize to the size below 1cm, then add 100ml of polytetrafluoroethylene together with the solution obtained in step (1) In the lining of the reaction kettle, ultrasonicate for 10min to make the mixing uniform;

[0041] (3) The reaction ...

Embodiment 2

[0049] Embodiment 2, FSHC and FHC product detection

[0050] The FSHC and FHC prepared in Example 1 were detected.

[0051] figure 1 and figure 2 The SEM images of FSHC and FHC are respectively. The Fe particles in FHC are successfully loaded on the hydrothermal carbon, but the particle size is large and it is easy to aggregate into agglomerates. Compared with FHC, due to the introduction of Ag, the Fe loading of FSHC is uniformly distributed on the hydrothermal carbon, with a particle size of about 100 nm and is not easy to aggregate into agglomerates.

[0052] The XRD scan results of FSHC are as follows image 3 As shown, 38.1°, 44.3°, 64.4°, and 77.4° correspond to the Ag(111), Ag(200), Ag(220), and Ag(311) crystal planes respectively (JCPDS No. 04-783), indicating that the silver particles are in the Biochar has been successfully doped with biochar during the preparation process; 34.3°, 57.8° correspond to Fe 3 O 4 (220) and (511) crystal planes (JCPDS No.19-0629), ...

Embodiment 3

[0055] Example 3, Cr(VI) removal experiment

[0056] Get the FSHC, FHC prepared in Example 1 for the treatment of Cr (VI)-containing waste water:

[0057] Take 0.04 g of the prepared FSHC and FHC materials and add them to a polyvinyl chloride centrifuge tube, and then add 40 mL of simulated wastewater containing 100 mg / LCr(VI) and a pH of 2, and quickly transfer them to an air-bath constant temperature oscillator. Adsorption at 25°C for 24h. The results showed that the adsorption capacities of FSHC and FHC materials for 100 mg / L Cr(VI) wastewater were 85.41 mg / g and 65.64 mg / g, respectively, and the leaching amounts of Fe in the solution after 24 h of reaction were 0.25 mg / L and 0.05 mg / L, respectively. , the Fe leaching amount of FSHC meets the drinking water standard (GB 5749-2006) of 0.3mg / L.

[0058] The initial pH is one of the important leading factors for the removal efficiency of Cr(VI) from water, which affects the degree of protonation of functional groups on the a...

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Abstract

The invention discloses a preparation method of iron-silver co-doped biochar with high adsorption capacity, which comprises the following steps: (1) preparing a mixed solution containing Fe ions and Ag ions: adding concentrated H3PO4, an iron compound and AgNO3 into an aqueous solution, and uniformly dispersing the solution; the iron compound is selected from ferric nitrate, ferrous nitrate or a mixture thereof; in the mixed solution, the mass ratio of the iron compound to AgNO3 is (10-50): 1; (2) crushing plant waste biomass, and adding the crushed plant waste biomass and the solution obtained in the step (1) into the lining of the reaction kettle; (3) putting the reaction kettle into a drying oven, raising the temperature to 180-230 DEG C, and maintaining the temperature for 1-2.5 hours; and (4) washing the material until the pH is close to neutral, and then drying. The preparation method disclosed by the invention is simple in steps, is completed by uniformly mixing the required raw materials and putting the mixture into a reaction kettle for one-step hydrothermal carbonization, is short in time consumption and low in chemical reagent consumption, and does not have the inherent problem of exhaust gas emission of a pyrolysis method.

Description

technical field [0001] The invention relates to the technical field of biochar preparation, in particular to an iron-silver co-doped biochar with high adsorption capacity and a preparation method thereof. Background technique [0002] The application of biochar in the field of water treatment has attracted more and more attention, and its abundant surface functional groups (carboxyl, hydroxyl, phenolic hydroxyl, etc.) are active sites for removing pollutants. In recent years, many scholars have greatly improved the adsorption performance of biochar by modifying biochar or loading metals. Especially after loading iron, not only the adsorption capacity is improved, but also the presence of iron endows biochar with magnetic properties, realizing the treatment of pollutants. The purpose of post-solid-liquid separation broadens the application scope of biochar. However, due to certain defects in the preparation technology, the biochar and the supported metals are easily leached,...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): B01J20/02B01J20/20B01J20/30C02F1/28C02F1/461B01J23/89C02F101/20C02F101/30
CPCB01J20/20B01J20/02B01J20/3078C02F1/46176C02F1/28C02F1/725C02F1/4672B01J23/8906B01J2220/4825C02F2101/30C02F2101/20Y02E50/10
Inventor 吴泽葵陈志莉周自坚方义李文斌张力钊
Owner GUILIN UNIVERSITY OF TECHNOLOGY
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