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A kind of preparation method of low-temperature ammonia removal catalyst

An ammonia catalyst and low-temperature technology, which is applied in the field of preparation of low-temperature ammonia removal catalysts, can solve the problems of low biological nitrogen removal efficiency, and achieve the effects of high nitrogen gasification degree of the product, simple and convenient preparation process, and low energy consumption

Active Publication Date: 2020-08-04
SHANXI UNIV
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0004] The invention aims at the problem of low biological denitrification efficiency under adverse conditions such as winter or low temperature in existing sewage treatment, and provides a preparation method of a low-temperature ammonia removal catalyst

Method used

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  • A kind of preparation method of low-temperature ammonia removal catalyst
  • A kind of preparation method of low-temperature ammonia removal catalyst

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0022] In this example, magnesium chloride and ferric chloride solutions with a concentration of 0.8mol / L were prepared respectively; under the condition of rapid stirring (200rpm), 500mL of magnesium chloride and ferric chloride solutions were mixed; Sodium silicate solution to pH 6.7, forming a colloidal precipitate, washed with pure water for 3 times, dried at 105°C, and crushed to 40 mesh or below 0.45mm in particle size, ready to use, to form component A; crushed to 40 mesh or Sodium silicate powder with a particle size below 0.45mm and starch are uniformly mixed at a mass ratio of 1% to form silicate starch; the straw is dried and crushed, and the fraction particles of 18-35 mesh are screened; the mass ratio is 4:2:4 Mix the above-mentioned granules with silicate starch and water, and stir well to make component B; take 30g of component A and 15g of component B, mix evenly and make 3~5mm particle size particles, and place them in a muffle furnace for anaerobic roasting at...

Embodiment 2

[0024] In this example, keep the temperature at 2-5°C, add 1 g of the above-mentioned catalyst C1 into the reactor, add 600 mL of ammonium sulfate solution with an ammonia nitrogen content of 50 mg / L (the pH of the solution is <5.9), and pass through ozone to make the solution The equilibrium concentration of ozone in the medium was maintained at 12 mg / L, and after shaking for 5 minutes, 10 minutes, and 60 minutes, samples were taken to determine the residual ammonia nitrogen content in the water. At the same time, under the same conditions, the ozone oxidation sample (pH9.0) was used as a control without adding a catalyst (ozone has almost no ability to oxidize and remove ammonia when the pH is lower than 7). The result is as follows:

[0025]

[0026] It can be seen that the effect of using the catalyst of the present invention to remove ammonia by catalytic oxidation is more than 4.7 times that of ozone oxidation alone, and the removal effect is good.

Embodiment 3

[0028] In this example, keep the temperature at 2-5°C, add 1 g of the above-mentioned catalyst C1 to the reactor, add 600 mL of ammonium sulfate solution with an ammonia nitrogen content of 63 mg / L, and inject ozone to keep the equilibrium concentration of ozone in the solution at 15 mg / L, shake the reaction for 5min, 10min, 60min and then take samples to measure the residual ammonia nitrogen and total nitrogen content in the water. At the same time, under the same conditions, the ozone oxidation sample (pH8.7) without catalyst was used as a control. The result is as follows:

[0029]

[0030] It can be seen that the catalytic oxidation group has a high removal rate of ammonia nitrogen, and the removal rate of total nitrogen is also significantly higher than that of the ozone control group.

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Abstract

A method for preparing a low-temperature ammonia removal catalyst, which belongs to the technical field of ammonia removal catalyst preparation. It can solve the problem of low biological denitrification efficiency in existing sewage treatment under unfavorable conditions such as winter or low temperature. The same molar concentration of magnesium salt solution and iron salt or ferrous salt solution, add sodium silicate solution dropwise to pH 6-7 to form a colloidal precipitate, dry it and crush it for use to form component A; mix a certain amount of sodium silicate powder and starch evenly to form silicic acid Starch; crush the straw to make granules; mix the above granules with silicate starch and water in a mass ratio of 4:2:4, stir thoroughly to make component B; take a certain amount of component A and component B and mix them evenly. Particles with a particle size of 3-5mm are made and placed in a muffle furnace for anaerobic roasting for 3 hours to generate a low-temperature ammonia removal catalyst. The ammonia nitrogen removal efficiency of the catalyst of the present invention is more than 4 times higher than that of ozone oxidation alone.

Description

technical field [0001] The invention belongs to the technical field of ammonia removal catalyst preparation, and in particular relates to a preparation method of a low-temperature ammonia removal catalyst. Background technique [0002] Ammonia nitrogen is a common pollutant in water and is strictly controlled. Ammonia nitrogen has important effects on aquatic organisms. High ammonia nitrogen promotes the growth of aquatic algae plants, and the excessive growth of planktonic algae such as blue-green algae causes water quality to deteriorate. Ammonia nitrogen inhibits the oxygen transfer of fish, which increases the cost of aquaculture, and even causes the loss of the whole dead pond in severe cases. Therefore, ammonia removal technology has a wide demand in water treatment, landscape water conservation, aquaculture and other aspects. At present, the main method for reducing ammonia nitrogen in sewage treatment plants is biological denitrification, which has the advantages ...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): B01J23/78C02F1/20C02F1/78C02F101/16
CPCC02F1/20C02F1/725C02F1/78B01J23/78C02F2101/16B01J35/50B01J35/40
Inventor 刘海龙
Owner SHANXI UNIV