Porous adsorbing material, oxygen-carrying and adsorbing composite functional material, and application of porous adsorbing material and oxygen-carrying and adsorbing composite functional material

A technology of porous adsorption material and matrix material, applied in the field of water body remediation materials, can solve the problems of reduced water body transparency, unsustainability, decline of aquatic animals and plants, etc., and achieves the effect of improving water body dissolved oxygen, good oxygen-carrying performance and water quality.

Active Publication Date: 2020-05-05
RES CENT FOR ECO ENVIRONMENTAL SCI THE CHINESE ACAD OF SCI
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  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

However, the passivation effect is affected by the pH value and redox state of the water body. When the pH value and redox state change, phosphorus is easily re-released to cause pollution.
At present, the internationally well-known "Phoslock" and other phosphorus fixative technologies use chemically modified clay minerals such as lanthanum and aluminum to cover the bottom mud to achieve the effect of fixing phosphorus in the bottom mud for a certain period of time and preventing it from being released again. This technology cannot effectively improve the anaerobic environment of polluted sediment, and has no effect on pollutants other than phosphorus, such as ammonia nitrogen, organic pollutants, heavy metals, etc., and the cost is very high
[0007] On the other hand, usually in polluted water bodies, due to unfavorable factors such as the reduction of water transparency, the decay and decomposition of organic matter in the bottom mud, including sedimentation algae and plant debris, etc., which consume a large amount of dissolved oxygen, the interior of the water body is often in an anaerobic or anoxic state.
Under anaerobic conditions, it will cause the release of endogenous pollutants, including the release of phosphate, iron, manganese, sulfur and other compounds that are sensitive to the redox environment as the dominant pollutants, which will further aggravate the deterioration of water quality and cause water pollution. Continued pollution will accelerate eutrophication and even the outbreak of algal blooms, which in turn will lead to further deterioration of the anaerobic state of the water environment, forming a vicious circle
This vicious cycle of "water quality deterioration - anaerobic water body and bottom - release of endogenous pollutants" not only leads to the decline of aquatic animals and plants, hinders the restoration of water environment, but even threatens the safety of drinking water and human health
[0008] However, there are still technical bottlenecks in the market for the anaerobic bottom of the water environment, especially the anaerobic bottom of the deep water and the anaerobic sediment.
The technologies commonly used in the market to improve bottom anaerobic can be divided into artificial aeration and hydraulic circulation. Artificial aeration includes surface aeration and deep aeration technology. The advantage is that it can quickly increase the dissolved oxygen in the water body, but the disadvantage is that it needs to consume Electric aeration equipment must operate continuously or intermittently. In practical applications, it is only suitable for small water bodies. The cost of large water areas is very high and it is not sustainable. Especially deep aeration often disturbs the sediment, causing a large amount of waste in the sediment Oxygen substances are resuspended, which consumes the oxygen in the water body instead, causing the dissolved oxygen to be lower than before the aeration after the aeration is stopped.
The hydraulic cycle includes two circulation methods, horizontal and vertical, which can exchange the water in the area with high dissolved oxygen and the water in the anaerobic area to improve the anaerobic problem at the bottom, but it often requires the continuous operation of high-power circulating water pumps. Applications are cost prohibitive and inefficient

Method used

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  • Porous adsorbing material, oxygen-carrying and adsorbing composite functional material, and application of porous adsorbing material and oxygen-carrying and adsorbing composite functional material
  • Porous adsorbing material, oxygen-carrying and adsorbing composite functional material, and application of porous adsorbing material and oxygen-carrying and adsorbing composite functional material
  • Porous adsorbing material, oxygen-carrying and adsorbing composite functional material, and application of porous adsorbing material and oxygen-carrying and adsorbing composite functional material

Examples

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Comparison scheme
Effect test

Embodiment 1

[0056] A kind of porous adsorption material is prepared according to the following steps:

[0057] 1) Wash natural zeolite, bentonite and fly ash with deionized water respectively, dry at 105°C, grind through a 50-mesh sieve, and set aside;

[0058] Get the zeolite, bentonite, and fly ash after the above-mentioned treatment and add aluminum chloride aqueous solution respectively, the solid-liquid ratio is respectively 1:5 (solid unit is g, liquid unit is ml), the concentration of used aluminum chloride aqueous solution is 1mol / L, pH is 8, oscillating and impregnating at 95°C for 24h, filtering, cooling the obtained residue, and drying; add sodium hydroxide aqueous solution to the dried material, and its solid-liquid ratio is 1:5 (solid unit is g, liquid unit is ml ), the concentration of the aqueous sodium hydroxide solution used is 1mol / L, shake and impregnate for 24h, filter, cool the gained solid, dry, and set aside;

[0059] 2) Take step 1) modified zeolite, bentonite an...

Embodiment 2

[0064] In this example, zeolite and fly ash were used to modify porous adsorption materials and oxygen-carrying + adsorption composite functional materials, and the porous adsorption materials were prepared according to the following steps:

[0065] 1) Natural zeolite, bentonite, and fly ash were washed with deionized water respectively, dried at 105°C, ground through a 100-mesh sieve, and set aside;

[0066] Get the zeolite, bentonite, and fly ash after the above-mentioned treatment and add aluminum chloride aqueous solution respectively, the solid-liquid ratio is respectively 1:6 (solid unit is g, liquid unit is ml), the concentration of used aluminum chloride aqueous solution is 2mol / L, the pH is 8, 95 ℃ shaking impregnation for 24h, filtering, cooling the obtained residue, and drying; add sodium hydroxide aqueous solution to the dried material, and its solid-liquid ratio is 1:6 (solid unit is g, liquid unit is ml ), the concentration of the aqueous sodium hydroxide soluti...

Embodiment 3

[0072] In this example, zeolite and fly ash were used to modify porous adsorption materials and oxygen-carrying + adsorption composite functional materials, and the porous adsorption materials were prepared according to the following steps:

[0073] 1) Natural zeolite, bentonite, and fly ash were washed with deionized water respectively, dried at 105°C, ground through a 150-mesh sieve, and set aside;

[0074] Get the zeolite, bentonite, and fly ash after the above-mentioned treatment and add aluminum chloride aqueous solution respectively, and its solid-liquid ratio is respectively 1:7 (solid unit is g, liquid unit is ml), and the concentration of aluminum chloride aqueous solution used is 3mol / L, pH is 7, oscillating and impregnating at 95°C for 24h, filtering, cooling the obtained residue, and drying; adding sodium hydroxide aqueous solution to the dried material, and its solid-liquid ratio is 1:7 (solid unit is g, liquid unit is ml), the concentration of aqueous sodium hyd...

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Abstract

The invention provides a porous adsorbing material, an oxygen-carrying and adsorbing composite functional material, and application of the porous adsorbing material and the oxygen-carrying and adsorbing composite functional material. Adoption of the oxygen-carrying and adsorption composite functional material in water body repairing can efficiently adsorb pollutants such as endogenous nitrogen andphosphorus in water body and improve the water body anaerobic problem and the like, the cost is low, and the ecological safety is very good. The composite functional material provided by the invention is prepared from porous particles prepared from a modified matrix material through pressure swing adsorption-oxygen loading, and the modified matrix material is obtained by sequentially dipping andmodifying a matrix material with a metal cation salt solution and an alkaline solution and then calcining the matrix material at a high temperature of 600-1000 DEG C; wherein the matrix material is selected from one or a combination of more than two of natural clay minerals, industrial solid wastes and activated carbon.

Description

technical field [0001] The invention belongs to the field of environmental science and engineering technology, and in particular relates to a water body restoration material prepared from natural and cheap materials and its application in water environment restoration. Background technique [0002] Water environmental pollution is one of the environmental problems attracting global attention. Even if the input of exogenous pollutants is effectively controlled, the internal source pollution accumulated in the water environment will cause the water body to be polluted for a long time. The oxygen environment exacerbates the risk of release of endogenous pollutants accumulated in the sediment into the water. [0003] Bottom mud, also known as sediment, is an important destination and reservoir for pollutants entering rivers, lakes and other surface water bodies, and is also the internal source of overlying water pollution. Especially when exogenous pollution is effectively cont...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): B01J20/20B01J20/16C02F1/28C02F1/68C02F3/02C02F11/00C02F11/02C02F101/16C02F101/10
CPCB01J20/12B01J20/20B01J20/16B01J20/165B01J20/103B01J20/08B01J20/06B01J20/0248B01J20/0288B01J20/041C02F1/283C02F1/281C02F1/68C02F3/02C02F11/00C02F11/02C02F2101/16C02F2101/105Y02W10/10
Inventor 张洪刚刘李璇潘纲陈俊
Owner RES CENT FOR ECO ENVIRONMENTAL SCI THE CHINESE ACAD OF SCI
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