A method and device for recovering metal oxides from waste flue gas denitrification catalyst

A denitrification catalyst and waste flue gas technology, applied in the direction of alkali metal compounds, titanium oxide/hydroxide, chemical instruments and methods, etc., can solve the problems of high consumption of raw materials, low extraction purity, complicated operation, etc., and improve the utilization rate Effect

Active Publication Date: 2017-07-28
CHINA HUADIAN ENG +1
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

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Problems solved by technology

But adopting above-mentioned high-temperature roasting method to reclaim the denitrification catalyst consumes more energy, is not suitable for suitability for industrialized production at all; The method for reclaiming the denitrification catalyst with lye treatment first, then with acid solution treatment, reagent waste is serious on the one hand (such as required lye is excessive , the excess lye is reused to neutralize the acid solution), which is not conducive to the effective utilization of resources. On the other hand, in the recovery process of the catalyst, Na 2 SiO 3 colloid, then when the solid-liquid separation is carried out by filtration, the colloid is easy to stay on the filter paper together with the precipitate, resulting in incomplete separation, which in turn leads to TiO 2 、WO 3 and V 2 o 5 The extraction purity is low, and the extraction efficiency is also low; in addition, in the prior art, the extraction method of titanium dioxide is mostly sodiumization first, and then adding sulfuric acid to gradually separate, which is complicated to operate and consumes more raw materials; it is directly recovered by acid solution treated denitrification catalysts, although their production of TiO 2 It can be connected with the production process of titanium dioxide, and the industrialization benefit is also obvious, but according to the record of CN 103130265 A, it can only convert TiO 2 with WO 3 , V 2 o 5 separated, while V 2 o 5 and WO 3 All belong to metal oxides with similar properties, and the waste flue gas denitrification catalyst contains TiO 2 and glass fiber mixture, so the V 2 o 5 and WO 3 It's not easy to separate

Method used

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  • A method and device for recovering metal oxides from waste flue gas denitrification catalyst
  • A method and device for recovering metal oxides from waste flue gas denitrification catalyst

Examples

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Embodiment 1

[0052] Embodiment 1 of the present invention: a method for recovering metal oxides from waste flue gas denitrification catalysts, such as figure 1 shown, including the following steps:

[0053] S01, blow the waste flue gas denitrification catalyst with compressed air for 20-23 minutes for each module to remove the dust in the channel;

[0054] S02, rinse the catalyst after dust removal with a high-pressure water gun, and rinse each module for 15-20 minutes, with a pressure of 8-12Mpa, to further remove the dust in the channel;

[0055] S03, drying the washed catalyst;

[0056] S1, pulverizing the catalyst and adding concentrated sulfuric acid for acidolysis, adding water after acidolysis to obtain a titanyl sulfate solution; specifically including the following steps:

[0057] S11, crushing the catalyst into catalyst powder of 160-180 mesh;

[0058] S12, put the catalyst powder into a lead-made acidolysis tank, add 88%-90% concentrated sulfuric acid according to the weight ...

Embodiment 2

[0071] Embodiment 2: a kind of method that recovers metal oxide from waste flue gas denitrification catalyst, such as figure 1 shown, including the following steps:

[0072] S01, blow the waste flue gas denitrification catalyst with compressed air, and blow each module for 15-20 minutes to remove the dust in the channel;

[0073] S02, rinse the catalyst after dust removal with a high-pressure water gun, and rinse each module for 20-25 minutes, with a pressure of 5-8Mpa, to further remove the dust in the channel;

[0074] S03, drying the washed catalyst;

[0075] S1, pulverizing the catalyst and adding concentrated sulfuric acid for acidolysis, adding water after acidolysis to obtain a titanyl sulfate solution; specifically including the following steps:

[0076] S11, crushing the catalyst into 180-200 mesh catalyst powder;

[0077] S12, put the catalyst powder into a lead-made acidolysis tank, add 85% to 88% concentrated sulfuric acid according to the weight ratio of cataly...

Embodiment 3

[0090] Embodiment 3: A method for recovering metal oxides from waste flue gas denitrification catalysts, such as figure 1 shown, including the following steps:

[0091] S01, blow the waste flue gas denitrification catalyst with compressed air for 23 to 30 minutes for each module to remove the dust in the tunnel;

[0092] S02, rinse the catalyst after dust removal with a high-pressure water gun, and rinse each module for 25 to 30 minutes, with a pressure of 7 to 10Mpa, to further remove the dust in the channel;

[0093] S03, drying the washed catalyst;

[0094] S1, pulverizing the catalyst and adding concentrated sulfuric acid for acidolysis, adding water after acidolysis to obtain a titanyl sulfate solution; specifically including the following steps:

[0095] S11, pulverizing the catalyst into 190 mesh catalyst powder;

[0096] S12, put the catalyst powder into a lead-made acidolysis tank, add 90% to 92% concentrated sulfuric acid according to the weight ratio of catalyst ...

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Abstract

The invention discloses a method and an apparatus for recycling metal oxide from a waste flue gas denitration catalyst. The method comprises the following steps: S1, the catalyst is crushed and concentrated sulfuric acid is added for acidolysis, after acidolysis, water is added to obtain a titanyl sulfate solution; S2, the titanyl sulfate solution is filtered, filter residues are standby, a filtrate is heated, condensed and hydrolyzed for obtaining a hydrolysate; S3, the hydrolysate is filtered to obtain a filtrate and a metatitanic acid deposition; S4, salt treatment, a drying and a calcination are carried out for the metatitanic acid deposition, and TiO2 is obtained; S5: sedimentation treatment is carried out for the filtrate in the S3, after filtering, a upper level clear liquid is taken, excessive NH4Cl is added into the clear liquid for reaction, after filtering, andammonium metavanadate deposition is obtained; the ammonium metavanadate deposition is calcined, and V2O5 is obtained; S6, excessive ammoniacal liquor is added into the filter residues in the S2 for reaction, and a filtering is carried out; a filtrate is heated to generate a ammonium paratungstate crystal; the ammonium paratungstate crystal is dried and calcined, and WO3 is obtained. According to the method, V, Ti and W three components can be completely separated.

Description

technical field [0001] The invention relates to a method and a device for recovering metal oxides from waste flue gas denitrification catalysts, and belongs to the technical field of waste flue gas denitrification catalyst recovery. Background technique [0002] SCR denitrification technology is a necessary means for power plants to achieve ultra-clean emissions. As the core part of SCR denitrification technology, the catalyst will lose its activity due to wear or blockage during operation. Partially regenerable catalysts can continue to be used after regeneration, while non-regenerable catalysts face the situation of rational utilization and disposal (even if regenerable catalysts are regenerated 2 to 3 times, they cannot be regenerated and need to be rationally utilized and disposed of). At present, landfill is the way to dispose of waste denitration catalysts in foreign countries, but there are many thermal power plants in my country, and the amount of waste denitration c...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): C01G31/02C01G41/02C01G23/053C01G49/14C01D5/00C04B35/66
CPCC01D5/00C01G23/0532C01G31/02C01G41/02C01G49/14C01P2006/80C04B35/66C04B2235/3218C04B2235/3418
Inventor 李苇林苏军划李伟胡永锋沈煜晖
Owner CHINA HUADIAN ENG
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