CN101811064A - Method for preparing composite catalyst for phosphine multi-phase oxidation - Google Patents

Method for preparing composite catalyst for phosphine multi-phase oxidation Download PDF

Info

Publication number
CN101811064A
CN101811064A CN201010145177A CN201010145177A CN101811064A CN 101811064 A CN101811064 A CN 101811064A CN 201010145177 A CN201010145177 A CN 201010145177A CN 201010145177 A CN201010145177 A CN 201010145177A CN 101811064 A CN101811064 A CN 101811064A
Authority
CN
China
Prior art keywords
nitrate
filter cake
phosphine
carrier
distilled water
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201010145177A
Other languages
Chinese (zh)
Inventor
黄小凤
刘伟文
宁平
谭娟
王小妮
李文卿
高琨阳
魏燕富
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kunming University of Science and Technology
Original Assignee
Kunming University of Science and Technology
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kunming University of Science and Technology filed Critical Kunming University of Science and Technology
Priority to CN201010145177A priority Critical patent/CN101811064A/en
Publication of CN101811064A publication Critical patent/CN101811064A/en
Pending legal-status Critical Current

Links

Images

Landscapes

  • Catalysts (AREA)

Abstract

The invention relates to a method for preparing a composite catalyst for phosphine multi-phase oxidation, which belongs to the technical field of industrial waste gas purification treatment. The method comprises the following steps: dissolving over two metal nitrates into distilled water to form composite metal ion solution; pre-treating a carrier, soaking the carrier into the metal ion solution with stirring, filtering the solution to obtain a filter cake, and drying the filter cake; placing the dried filter cake in a roasting furnace to perform roasting; and cooling and screening the roasted filter cake to obtain a catalyst product. The method is convenient and quick; and the prepared composite catalyst can obviously improve the absorption efficiency of hydrogen peroxide solution on phosphine, has good stability, no impurity and little using amount, and can be repeatedly used.

Description

A kind of method for preparing composite catalyst that is used for phosphine multi-phase oxidation
Technical field
The present invention relates to a kind of method for preparing composite catalyst that is used for phosphine multi-phase oxidation, belong to the industrial waste gas purifying processing technology field.
Background technology
In phosphorus production, can produce a kind of waste residue of forming by element phosphor, dust impurity and water-mud phosphorus.In order to reclaim the phosphorus in the mud phosphorus, studies show that adopting mud phosphorus and alkaline reaction to produce sodium hypophosphite is a kind of effective governing measure, its reaction temperature is not high, energy resource consumption is little, and sodium hypophosphite is as a kind of reducing agent, be widely used in industries such as chemical plating, plating, machinery, food processing, have higher economic value added.But this improvement method will make in the mud phosphorus about 20% phosphorus simple substance be converted into hydrogen phosphide and enter into tail gas, if it is not handled, then can cause atmosphere pollution.
Hydrogen phosphide is colourless, garlic smell is arranged.But as be mixed with a small amount of poly-hydrogen phosphide spontaneous combustion, can blast when concentration acquires a certain degree, hydrogen phosphide has strong reducing property, can with many oxidant reduction reactions, as KMnO 4, I 2Hydrogen phosphide has hypertoxicity, when phosphine concentration is 10mgm -3The time, human body contact 6h can have poisoning symptom.Concentration is 409~846mgm -3The time, contact 0.5~1.0h can cause death.The method of purifying hydrogen phosphide is a lot of both at home and abroad, mainly is divided into two kinds of dry method and wet methods.The selection of various purification methods is decided according to the character and the source of waste gas, and the phosphine waste gas low for concentration, that total amount is few often adopts absorption method; Big normal employing absorbs oxidizing process and reclaims wherein phosphor resource for concentration height, total amount.
It is higher that mud phosphorus is produced the phosphine waste gas concentration that sodium hypophosphite produces, be fit to adopt hydrogenperoxide steam generator as absorption liquid, make the hydrogen phosphide in the tail gas be oxidized to sodium hypophosphite with absorbing this waste gas of oxidative treatment, thereby increase the output of sodium hypophosphite product, resource is rationally utilized.Find in the practical application, absorb hydrogen phosphide tail gas,, make absorption efficiency on the low side because its reaction speed is slower with hydrogen peroxide.Therefore, must add catalyst and come fast reaction speed, improve absorption efficiency.
Summary of the invention
The purpose of this invention is to provide a kind of method for preparing composite catalyst that is used for phosphine multi-phase oxidation, multiple metal ion has synergy, solidification, peptizaiton in the prepared catalyst, can improve the catalytic efficiency and the stability of catalyst, can obviously improve the absorption efficiency of hydrogenperoxide steam generator to hydrogen phosphide, and catalyst amount is less, and is reusable.
The present invention is achieved through the following technical solutions: two or more nitrate are dissolved in the distilled water, are made into metal ion solution; Carrier carries out preliminary treatment earlier, is immersed in the metal ion solution under stirring then, filters and obtains filter cake, again oven dry; Place roaster to synthesize dried filter cake, obtain catalyst prod.
Concrete technical scheme of the present invention is:
(1) nitrate adopts be in ferric nitrate, copper nitrate, zinc nitrate, silver nitrate, the cerous nitrate more than two kinds,, the metal ion solution concentration that is made into is 0.01~1mol/L; (2) carrier is any in granularity 40~180 purpose powdery zeolites, diatomite, active carbon, activated alumina, the rice hull ash; (3) flood in the metal ion solution that carrier 1: 5 by volume~30 addings prepare; (4) sintering temperature of roaster is that 250~800 ℃, insulation synthesized in 2~6 hours, obtains catalyst through screening then.
In the NaOH of 0.1mol/L solution, soaked 1 hour earlier during the carrier preliminary treatment, use the distilled water cyclic washing then, the HCl solution with 0.1mol/L soaked 1 hour again, soaked back distilled water cyclic washing, used distilled water immersion at last 1 hour, and filtered the back and dry 12h down at 105~130 ℃; Carrier impregnation is to stir at normal temperatures 4~6 hours, floods then 18~20 hours, filters at last, obtains filter cake and dries 1~3 hour again.
The present invention has the following advantages:
(1) add catalyst of the present invention, hydrogenperoxide steam generator obviously improves the absorption efficiency of hydrogen phosphide;
(2) have synergy, solidification, peptizaiton between each metal ion of composite catalyst, the composite catalyst stability that makes better with solid-state adding, is not brought other impurity into;
(3) the composite catalyst consumption is less, and reusable.
Description of drawings:
Fig. 1 is the process chart of invention Preparation of Catalyst;
Fig. 2 is an invention hydrogen phosphide heterogeneous catalytic oxidation process chart;
Fig. 3 is the assimilation effect figure of invention example 1;
Fig. 4 is the assimilation effect figure of invention example 2;
Fig. 5 is the assimilation effect figure of invention example 3.
The specific embodiment:
Example 1: ferric nitrate, cerous nitrate are dissolved in the distilled water with mol ratio at 1: 1, are made into the solution that concentration of metal ions is 0.01mol/L; With particle diameter is 180 purpose 4A zeolites, in the sodium hydroxide solution of 0.1mol/L, soaked 1 hour, soak the back repeatedly with the distilled water cyclic washing, hydrochloric acid solution with 0.1mol/L soaked 1 hour again, soak the back repeatedly with the distilled water cyclic washing, used distilled water immersion at last 1 hour, and filtered the back and dried 12 hours down at 105 ℃; Through after the preliminary treatment, add at 1: 5 in the solution for preparing according to the solid-liquid mass ratio, normal temperature stirred 4 hours down, flooded then 20 hours, filtered at last; Filter cake after the oven dry is placed roaster, and sintering temperature is 250 ℃, is incubated 6 hours, and screening obtains 180 purpose catalyst; The catalyst that makes is added in hydrogenperoxide steam generator with mass ratio at 1: 200.The material of reactor is mud phosphorus 10.01g (phosphorus content 45.2%), alkali lye 180mL (containing NaOH 7.26g, calcium hydroxide 1.43g) during the preparation sodium hypophosphite; Carrier gas is a nitrogen, and flow velocity is 20mL/min; Gas washing liquid is selected 85% SPA 100mL for use; Absorption liquid is 6% hydrogenperoxide steam generator 100mL, and to regulate the absorption liquid pH value with the 0.1mol/L sodium hydroxide solution be 14.
Hydrogenperoxide steam generator is seen Fig. 3 to the assimilation effect of hydrogen phosphide, and sodium hypophosphite output is 1.4587g behind the absorption 6h, and the conversion ratio of phosphorus is 47.14%.
Example 2: ferric nitrate, zinc nitrate, copper nitrate are dissolved in the distilled water with mol ratio at 2: 1: 1, are made into the solution that concentration of metal ions is 0.5mol/L; With particle diameter is 110 purpose rice hull ash, in the sodium hydroxide solution of 0.1mol/L, soaked 1 hour, soak the back repeatedly with the distilled water cyclic washing, hydrochloric acid solution with 0.1mol/L soaked 1 hour again, soak the back repeatedly with the distilled water cyclic washing, used distilled water immersion at last 1 hour, and filtered the back and dried 12 hours down at 118 ℃; Through after the preliminary treatment, add at 1: 18 in the solution for preparing according to the solid-liquid mass ratio, normal temperature stirred 5 hours down, flooded 19 hours, filtered at last; Filter cake after the oven dry is placed roaster, and sintering temperature is 525 ℃, is incubated 4 hours, and screening obtains 110 purpose catalyst; The catalyst that makes is added in hydrogenperoxide steam generator with mass ratio at 1: 100.The material of reactor is mud phosphorus 10.05g (phosphorus content 45.3%), alkali lye 175mL (containing NaOH 7.22g, calcium hydroxide 1.44g) during the preparation sodium hypophosphite; Carrier gas is a nitrogen, and flow velocity is 20mL/min; Gas washing liquid is selected 85% SPA 100mL for use; Absorption liquid is 6% hydrogenperoxide steam generator 100mL, and to regulate the absorption liquid pH value with sodium hydroxide solution be 13.
Hydrogenperoxide steam generator is seen Fig. 4 to the assimilation effect of hydrogen phosphide, and sodium hypophosphite output is 1.2356g behind the absorption 6h, and the conversion ratio of phosphorus is 39.69%.
Example 2: with ferric nitrate, cerous nitrate, silver nitrate, copper nitrate with mol ratio 4: 4: 1: 2 are dissolved in the distilled water, are made into the solution that concentration of metal ions is 1mol/L; With particle diameter is 40 purpose active carbons, in the sodium hydroxide solution of 0.1mol/L, soaked 1 hour, soak the back repeatedly with the distilled water cyclic washing, hydrochloric acid solution with 0.1mol/L soaked 1 hour again, soak the back repeatedly with the distilled water cyclic washing, used distilled water immersion at last 1 hour, and filtered the back and dried 12 hours down at 130 ℃; Through after the preliminary treatment, add at 1: 30 in the solution for preparing according to the solid-liquid mass ratio, normal temperature stirred 6 hours down, flooded 18 hours, filtered at last; Filter cake after the oven dry is placed roaster, and sintering temperature is 800 ℃, is incubated 2 hours, and screening obtains 40 purpose catalyst; The catalyst that makes is added in hydrogenperoxide steam generator with mass ratio at 1: 100.The material of reactor is mud phosphorus 9.98g (phosphorus content 45.3%), alkali lye 175mL (containing NaOH 7.22g, calcium hydroxide 1.44g) during the preparation sodium hypophosphite; Carrier gas is a nitrogen, and flow velocity is 20mL/min; Gas washing liquid is selected 85% SPA 100mL for use; Absorption liquid is 6% hydrogenperoxide steam generator 100mL, and to regulate the absorption liquid pH value with sodium hydroxide solution be 13.
Hydrogenperoxide steam generator is seen Fig. 5 to the assimilation effect of hydrogen phosphide, and sodium hypophosphite output is 1.2034g behind the absorption 6h, and the conversion ratio of phosphorus is 38.92%.

Claims (3)

1. a method for preparing composite catalyst that is used for phosphine multi-phase oxidation is characterized in that: two or more nitrate are dissolved in the distilled water, are made into metal ion solution; Carrier carries out preliminary treatment earlier, is immersed in the metal ion solution under stirring then, filters and obtains filter cake, again oven dry; Place roaster to synthesize dried filter cake, obtain catalyst prod.
2. by the described method for preparing composite catalyst that is used for phosphine multi-phase oxidation of claim 1, it is characterized in that: (1) nitrate adopts be in ferric nitrate, copper nitrate, zinc nitrate, silver nitrate, the cerous nitrate more than two kinds, the metal ion solution concentration that is made into is 0.01~1mol/L; (2) carrier is any in granularity 40~180 purpose powdery zeolites, diatomite, active carbon, activated alumina, the rice hull ash; (3) flood in the metal ion solution that carrier 1: 5 by volume~30 addings prepare; (4) sintering temperature of roaster is that 250~800 ℃, insulation synthesized in 2~6 hours, obtains catalyst through screening then.
3. by the described method for preparing composite catalyst that is used for phosphine multi-phase oxidation of claim 2, it is characterized in that: in the NaOH of 0.1mol/L solution, soaked 1 hour earlier during the carrier preliminary treatment, use the distilled water cyclic washing then, HCl solution with 0.1mol/L soaked 1 hour again, soak back distilled water cyclic washing, used distilled water immersion at last 1 hour, and filtered the back and dry 12h down at 105~130 ℃; Carrier impregnation is to stir at normal temperatures 4~6 hours, floods then 18~20 hours, filters at last, obtains filter cake and dries 1~3 hour again.
CN201010145177A 2010-04-13 2010-04-13 Method for preparing composite catalyst for phosphine multi-phase oxidation Pending CN101811064A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201010145177A CN101811064A (en) 2010-04-13 2010-04-13 Method for preparing composite catalyst for phosphine multi-phase oxidation

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201010145177A CN101811064A (en) 2010-04-13 2010-04-13 Method for preparing composite catalyst for phosphine multi-phase oxidation

Publications (1)

Publication Number Publication Date
CN101811064A true CN101811064A (en) 2010-08-25

Family

ID=42618517

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201010145177A Pending CN101811064A (en) 2010-04-13 2010-04-13 Method for preparing composite catalyst for phosphine multi-phase oxidation

Country Status (1)

Country Link
CN (1) CN101811064A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102240499A (en) * 2011-07-15 2011-11-16 田琳 Composite absorbing agent for processing hydrogen phosphide gas and preparation method thereof
CN111375291A (en) * 2018-12-31 2020-07-07 中国石油化工股份有限公司 Treatment method of sulfide-containing organic waste gas

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
QIONGFEN YU ET AL.: "Study of PH3 Adsorption and Regeneration over CuO-ZnO-La2O3/Activated Carbon Adsorbents", 《POWER AND ENERGY ENGINEERING CONFERENCE(APPEEC),2010 ASIA-PACIFIC》 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102240499A (en) * 2011-07-15 2011-11-16 田琳 Composite absorbing agent for processing hydrogen phosphide gas and preparation method thereof
CN102240499B (en) * 2011-07-15 2013-06-12 田琳 Composite absorbing agent for processing hydrogen phosphide gas and preparation method thereof
CN111375291A (en) * 2018-12-31 2020-07-07 中国石油化工股份有限公司 Treatment method of sulfide-containing organic waste gas

Similar Documents

Publication Publication Date Title
CN105056882A (en) Preparation method of modified charcoal-based adsorbent for removing hydrogen sulfide
CN102423688B (en) Preparation method for walnut shell active carbon adsorbent for purifying low concentration phosphine
CN105565465A (en) Method for treating phthalate wastewater by means of catalyzing persulfate by utilization of supported activated carbon in microwave inducement manner
CN105457643A (en) Preparation method of active carbon loaded catalyst for electrochemically catalyzing and degrading organic wastewater
CN102941084A (en) Method for preparing double-component metallic oxide catalytic ozonation catalyst
CN110743549B (en) Preparation method of copper-based heterogeneous catalyst taking activated carbon spheres as carrier for wet oxidation
CN104492425A (en) Catalyst for ammonia selective reduction of nitrogen oxide and preparation method of catalyst
CN103191764B (en) Mercury-free catalyst for synthesizing vinyl chloride through acetylene hydrochlorination and preparation method thereof
CN104841441B (en) The method for preparing catalyst of hydrolysis oxidation coupled method purification HCN a kind of and application
CN102000548A (en) Method for preparing modified active carbon adsorbent of low-concentration organic waste gas
CN106964333B (en) Rare earth supported catalyst for treating sewage, preparation method and application thereof, and method for treating sewage by catalytic oxidation of ozone
CN114832838B (en) Metal/sulfur-persulfate loaded biochar composite material and preparation and application thereof
CN109985616A (en) Catalyst for photocatalytic degradation of organic wastewater and preparation method thereof
CN113104928B (en) Application of CuO @ nitrogen doped carbon composite catalytic material in photo-thermal catalysis for producing non-free radicals
CN104190358A (en) NOx adsorber
CN101804362A (en) Microwave synthesis method used for multi-phase oxidation catalyst of hydrogen phosphide
CN103406021A (en) Method for removing phosphine through double liquid phases
CN101811064A (en) Method for preparing composite catalyst for phosphine multi-phase oxidation
CN111804300B (en) Ozone oxidation catalyst for advanced treatment of organic wastewater and preparation method thereof
CN105056950B (en) A kind of microwave based on coal-based carbon takes off NOx catalyst and preparation method thereof
CN101798092A (en) Polyferro-silicate, preparation method thereof and applications thereof in water treatment
CN106732522A (en) The preparation method of carrying transition metal oxide catalyst
CN102188979B (en) Smoke denitration catalyst by catalytic oxidation, and preparation method thereof
CN106732542A (en) One-step method prepares sheet manganese dioxide/carbon fibers at low temperature denitrating catalyst
CN101318124A (en) Method for preparing molecular sieve adsorption agent for low-concentration hydrogen phosphide purification

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20100825