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Amorphous iron-manganese colloid material as well as preparation method and application thereof

A colloidal material and amorphous technology, which is applied in the field of arsenic and antimony contaminated soil treatment, can solve the problems of rarely used soil remediation, and achieve the effect of easy large-scale production, excellent effect, and wide range of pH application

Active Publication Date: 2022-07-05
CENT SOUTH UNIV
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

However, these materials are mostly used in water treatment, and rarely used in the remediation of arsenic and antimony contaminated soil

Method used

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  • Amorphous iron-manganese colloid material as well as preparation method and application thereof
  • Amorphous iron-manganese colloid material as well as preparation method and application thereof
  • Amorphous iron-manganese colloid material as well as preparation method and application thereof

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0052] After washing with water to remove impurities such as sediment and sand attached to the surface, drying at 60°C, grinding, and sieving 5g of 40-mesh spent grains into the ball mill tank, adding grinding balls at a ratio of 15:1, the ball mill is an omnidirectional Planetary ball mill, set the ball milling speed to 320 rpm, after ball milling for 8 hours, sieve through 100 meshes, then disperse into 1L of 100 ℃ boiling deionized water and stir for 30 minutes, then filter and cool to room temperature to obtain the spent grains extract ( 0.5 wt%). After that, 2.8 g of ferrous sulfate heptahydrate and 0.2 g of potassium permanganate were respectively dissolved in 100 mL of the spent grains leaching solution. Secondly, under magnetic stirring at 200 rpm, the ferrous sulfate solution of wheat spent grains was slowly added to the potassium permanganate wheat spent solution, and at the same time, the pH was adjusted to 7.5 with 0.5 mol / L sodium hydroxide. The system continued ...

Embodiment 2

[0054] Since iron and manganese oxides are easy to agglomerate, this example compares the suspended state of iron and manganese oxides modified by different dispersants. The specific method is as follows: the synthetic method of modified iron manganese oxide without adding dispersant is as follows: dissolve 2.8g ferrous sulfate heptahydrate and 0.2g potassium permanganate into 100ml deionized water respectively, stir magnetically at 200rpm until completely dissolved, Under magnetic stirring, the ferrous sulfate solution was slowly added to the potassium permanganate solution, and the pH was adjusted to 7.5 with 0.5mol / L sodium hydroxide. . The rest of the carboxymethyl cellulose (CMC); rhamnolipid; xanthan gum; starch and wheat grains leaching solution (treated with Example 1) modified iron manganese oxide synthesis method: 2.8g ferrous sulfate seven Hydrate and 0.2g potassium permanganate were dissolved in 100ml of 0.5wt% carboxymethyl cellulose (CMC); rhamnolipid; xanthan g...

Embodiment 3

[0056] 2.516; 2.621; 2.8; 2.862 g of ferrous sulfate heptahydrate and 0.484; 0.378; 0.2; 0.138 g of potassium permanganate were dissolved in 100 mL of 0.5 wt % spent grains leaching solution respectively. Secondly, under magnetic stirring at 200 rpm, the ferrous sulfate solution of wheat spent grains was slowly added to the potassium permanganate wheat spent solution, and at the same time, the pH was adjusted to 7.5 with 0.5 mol / L sodium hydroxide. The system continued to stir for 2 hours to obtain amorphous iron-manganese colloidal materials with iron and manganese molar ratios of 3:1; 4:1; 8:1; 12:1, respectively, and the iron ion concentrations were 0.045; 0.047; 0.05; 0.051mol / L, respectively .

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Abstract

The invention discloses an amorphous iron-manganese colloid material as well as preparation and application thereof. The preparation method of the amorphous iron-manganese colloidal material comprises the following steps: mixing the spent grain leachate with ferric salt and manganese salt, adjusting the pH value, uniformly mixing and reacting to obtain the amorphous iron-manganese colloidal material, and preferably, carrying out ball milling and hydrothermal reaction on the spent grain leachate to obtain the amorphous iron-manganese colloidal material. The method is low in process energy consumption, short in preparation period, simple and controllable and capable of achieving large-scale programmed production, the prepared amorphous iron-manganese colloid material has good migration performance and can be applied to synchronous in-situ stable remediation of soil arsenic and antimony pollution, the remediation material is added into actual arsenic and antimony combined contaminated site soil, and the remediation effect is good. The fixing rates of water-soluble arsenic and antimony can reach 100%, and the fixing rates of effective arsenic and antimony can reach 82.54% and 52.59% respectively.

Description

technical field [0001] The invention belongs to the field of arsenic and antimony polluted soil treatment, and in particular relates to an amorphous iron-manganese colloidal material used for in-situ repair of arsenic and antimony polluted soil and its preparation and application. Background technique [0002] Existing in-situ remediation technologies for heavy metal-contaminated soils mainly include physical remediation, chemical remediation, phytoremediation, microbial remediation, and joint remediation. These remediation methods can achieve the effect of removing pollutants quickly and efficiently, but these remediation techniques have different degrees of limitations. Removal of soil and soil remediation are costly and have the risk of secondary pollution. Electric remediation technology is only suitable for small areas of pollution, and it is difficult to operate on-site; phytoremediation technology takes a long time, and high-concentration pollution levels are not cond...

Claims

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Application Information

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IPC IPC(8): C09K17/02C09K17/40B09C1/00B09C1/08
CPCC09K17/02C09K17/40B09C1/00B09C1/002B09C1/08B09C2101/00
Inventor 杨卫春郑钧浩聂开张煜镓姜智杨志辉廖骐司梦莹赵飞平
Owner CENT SOUTH UNIV