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a mno 2 Preparation method and application of coal-ldo low-temperature flue gas denitrification catalyst

A denitration catalyst, low temperature flue gas technology, applied in catalyst activation/preparation, metal/metal oxide/metal hydroxide catalyst, physical/chemical process catalyst, etc. The high temperature of the working window can achieve the effect of good water resistance and sulfur resistance, good thermal stability and large specific surface area.

Active Publication Date: 2021-05-18
TAIYUAN UNIV OF TECH
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

At present, the V-W-Ti system and its modified catalysts are relatively mature in this application field. However, the working window temperature for its excellent catalytic performance is relatively high (300-400 ℃), which cannot well meet the working conditions such as low temperature and wide working temperature window. Therefore, the research and development of a new type of vanadium-free, low-temperature, high-efficiency, and stable performance environment-friendly catalyst that matches the actual working conditions has become a hot spot in the field of this technology research.

Method used

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  • a mno  <sub>2</sub> Preparation method and application of coal-ldo low-temperature flue gas denitrification catalyst
  • a mno  <sub>2</sub> Preparation method and application of coal-ldo low-temperature flue gas denitrification catalyst
  • a mno  <sub>2</sub> Preparation method and application of coal-ldo low-temperature flue gas denitrification catalyst

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0051] (1) Weigh 4.37 g of cobalt nitrate nonahydrate and 1.87 g of aluminum nitrate nonahydrate into a beaker, add 80.0 mL of deionized water into the beaker, stir with a magnetic stirrer for 10 min to completely dissolve, and set aside;

[0052] (2) Weigh 0.80 g of hexamethylenetetramine, and add 56.0 mL of deionized water into a beaker to prepare it to a concentration of 0.10 mol L -1 The hexamethylenetetramine solution, stand-by;

[0053] (3) Add the above-prepared hexamethylenetetramine solution into the above-prepared mixed nitrate solution, stir vigorously at 800 r / min for 30 min, and then seal the obtained precipitate and mother liquor in polytetrafluoroethylene In a stainless steel reaction kettle lined with vinyl fluoride, heat in an oven at 140 °C for 12 h;

[0054] (4) After the reaction kettle was naturally cooled, the reacted solution was suction-filtered to obtain a precipitate, which was washed with deionized water several times until neutral, and dried in an ...

Embodiment 2

[0064] (1) Weigh 2.91 g of cobalt nitrate nonahydrate and 1.87 g of aluminum nitrate nonahydrate into a beaker, add 70.0 mL of deionized water into the beaker, stir with a magnetic stirrer for 10 min to completely dissolve, and set aside;

[0065] (2) Weigh 0.61 g of hexamethylenetetramine, and add 45.0 mL of deionized water into a beaker to prepare it to a concentration of 0.10 mol L -1 The hexamethylenetetramine solution, stand-by;

[0066] (3) Add the above-prepared hexamethylenetetramine solution into the above-prepared mixed nitrate solution, stir vigorously at 800 r / min for 30 min, and then seal the obtained precipitate and mother liquor in polytetrafluoroethylene In a stainless steel reaction kettle lined with vinyl fluoride, heat in an oven at 140 °C for 12 h;

[0067] (4) After the reaction kettle is naturally cooled, filter the reacted solution to get the precipitate, wash it with deionized water several times until neutral, put it in an oven for 12 h at 60 °C, grin...

Embodiment 3

[0073] (1) Weigh 4.37 g of cobalt nitrate nonahydrate and 1.87 g of aluminum nitrate nonahydrate into a beaker, add 80.0 mL of deionized water into the beaker, stir with a magnetic stirrer for 10 min to completely dissolve, and set aside;

[0074] (2) Weigh 0.80 g of hexamethylenetetramine, and add 56.0 mL of deionized water into a beaker to prepare it to a concentration of 0.10 mol L -1 The hexamethylenetetramine solution, stand-by;

[0075] (3) Add the above-prepared hexamethylenetetramine solution into the above-prepared mixed nitrate solution, stir vigorously at 800 r / min for 30 min, and then seal the obtained precipitate and mother liquor in polytetrafluoroethylene In a stainless steel reaction kettle lined with vinyl fluoride, heat in an oven at 140 °C for 12 h;

[0076] (4) After the reaction kettle is naturally cooled, filter the reacted solution to get the precipitate, wash it with deionized water several times until neutral, put it in an oven for 12 h at 60 °C, grin...

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Abstract

The invention discloses a kind of MnO 2 Preparation method and application of CoAl‑LDO low temperature flue gas denitrification catalyst. Using cobalt nitrate nonahydrate and aluminum nitrate nonahydrate as raw materials, and hexamethylenetetramine (HMT) as precipitating agent, the CoAl-based aqueous solution for nitrate intercalation is prepared by preparing solution, hydrothermal treatment, suction filtration, washing and drying. Talc precursor (CoAl‑NO 3 ‑LDH); then use permanganate as the target anion and oxidant, through ion exchange and redox reaction, suction filtration, washing, and drying, to obtain MnO 2 Intercalated CoAl-hydrotalcite-like (CoAl‑MnO 2 ‑LDH); finally roasted to get MnO 2 / CoAl‑LDO low temperature flue gas denitrification catalyst. The catalyst is used in low temperature (90~300℃) selective catalytic reduction of ammonia (NH 3 ‑SCR) denitrification reaction showed good catalytic activity, high N 2 Selectivity and good water and sulfur resistance.

Description

technical field [0001] The invention belongs to the field of gas purification and denitrification catalyst preparation, and specifically relates to a kind of MnO 2 Preparation method and application of CoAl-LDO low temperature flue gas denitrification catalyst. Background technique [0002] Nitrogen oxides (NO x ) as the main pollutant in the atmosphere seriously affects the ecological environment and endangers human health. With the enhancement of public awareness of environmental protection and the strict tightening of regulations and policies, the efficient removal and emission reduction of nitrogen oxides has become a severe situation faced by relevant industrial production units. Ammonia selective catalytic reduction technology (NH 3 -SCR) has become a popular and highly efficient denitrification technology at home and abroad because the reaction conditions are easy to control, and has been widely used in production practice. At present, the V-W-Ti system and its mo...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): B01J23/889B01J37/30B01J37/08B01J37/10B01D53/86B01D53/56
CPCB01D53/8628B01D2258/0283B01J23/8892B01J37/08B01J37/10B01J37/30
Inventor 吴旭杜亚丽冯雅琳刘江宁刘利利
Owner TAIYUAN UNIV OF TECH