CN106145172A - A kind of water purification agent and preparation method thereof - Google Patents

A kind of water purification agent and preparation method thereof Download PDF

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Publication number
CN106145172A
CN106145172A CN201610497458.1A CN201610497458A CN106145172A CN 106145172 A CN106145172 A CN 106145172A CN 201610497458 A CN201610497458 A CN 201610497458A CN 106145172 A CN106145172 A CN 106145172A
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China
Prior art keywords
water
water purification
purification agent
temperature
reaction
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CN201610497458.1A
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Chinese (zh)
Inventor
祝汉国
仉杰
梁昌峰
张新功
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Qingdao Hui Cheng Environmental Technology Co Ltd
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Qingdao Hui Cheng Environmental Technology Co Ltd
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Priority to CN201610497458.1A priority Critical patent/CN106145172A/en
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    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F7/00Compounds of aluminium
    • C01F7/68Aluminium compounds containing sulfur
    • C01F7/74Sulfates
    • C01F7/76Double salts, i.e. compounds containing, besides aluminium and sulfate ions, only other cations, e.g. alums
    • C01F7/762Ammonium or alkali metal aluminium sulfates
    • C01F7/765Ammonium aluminium sulfates
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • C02F1/5245Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Geology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Catalysts (AREA)

Abstract

Disclosed herein is a kind of water purification agent and preparation method thereof, belong to water purification agent preparing technical field, fall within solid waste process and utilize field.Raw material used in the present invention is particle diameter < the microspheroidal catalytic cracking spent catalyst of 200 μm, mainly comprising as silicon oxide and aluminium oxide of this dead catalyst.Concrete operations include: (1) < the microspheroidal catalytic cracking spent catalyst of 200 μm is pulled an oar together with water, and stirring (2) is 20%~65% according to course of reaction acid concentration, and the ratio of solid-to-liquid ratio 1:2 6 adds sulphuric acid by particle diameter;(3) regulating reaction temperature after acid adding is 90 150 DEG C, reacts 1 6h at this temperature;(4) reaction is diluted with water to 2~3 times of original volume after terminating, and when temperature is not less than 90 DEG C, centrifugal filtration obtains filtrate;(5) in filtrate, it is passed through ammonia or adds ammonium sulfate, being cooled to 0~60 DEG C, filtering, washing, obtain water purifying granular agent Burnt ammonium alum crude product after drying;(6) technical grade Burnt ammonium alum is obtained after recrystallization.The present invention utilizes catalytic cracking spent catalyst produced by each refinery to prepare water purification agent for raw material production, has both obtained new product, solves again a process difficult problem for solid waste, economy environmental protection again.

Description

A kind of water purification agent and preparation method thereof
Technical field
The present invention relates to a kind of water purification agent and preparation method thereof, belong to water purification agent technical field, fall within solid waste Process utilizes field.
Background technology
Water purification agent is a kind of medicament can put into and react with other impurity in water in water, because it is of a great variety, Preparation method also differs the biggest.
In recent years, along with the increase of industrial waste generation amount, Many researchers utilizes the industrial waste containing aluminum to prepare respectively Plant the product of relevant aluminum, these products have a lot all about water purification agent.
Chinese patent CN104803438A discloses and a kind of utilizes coal ash for manufacturing to obtain for the method for water purification agent, the method Harmful substance in polluted-water can be carried out adsorbing, flocculate, precipitate and separating by water purification agent effectively, it is achieved purifying water effect.
Chinese patent CN102887578A discloses a kind of method utilizing dead catalyst production waste flocculant, the method Selecting the high magnetic catalyst after Magneto separate is that polyaluminium chloride flocculant prepared by raw material, and the process both having solved dead catalyst is difficult Topic, achieves again the production of flocculant.
Chinese patent CN102560129A discloses a kind of method preparing high purity aluminium oxide from useless aluminium-based catalyst, should Method is Roasting And Leaching dealuminzation from the useless aluminium-based catalyst containing noble metal, first obtains Burnt ammonium alum, and after recrystallization, calcining obtains height Pure alumina.
Though there being many reports to reclaim the aluminum method for water purification agent from waste material, but there are no report to be mainly composed of Aluminium oxide and silicon oxide, < the microspheroidal catalytic cracking spent catalyst of 200 μm is the method that raw material preparation synthesizes water purification agent to particle diameter. The granule of this particle diameter suspends contaminated air in atmosphere, increases haze and produces probability, therefore, be badly in need of working out a kind of simple easily This particle diameter that solves of row is that < process of the microspheroidal catalytic cracking spent catalyst of 200 μm utilizes.
Summary of the invention
For the problems referred to above, the technical problem to be solved in the present invention is to provide a kind of by particle diameter < the microspheroidal catalysis of 200 μm Cracking dead catalyst prepares the method for water purification agent.
The invention mainly comprises following step:
(1) by particle diameter, < the microspheroidal catalytic cracking spent catalyst of 200 μm is pulled an oar together with water, stirs 30min;
(2) being 20%~65% according to course of reaction acid concentration, the ratio of solid-to-liquid ratio 1:2-6 adds sulphuric acid;
(3) regulate reaction temperature after acid adding and be 90-150 DEG C, react 1-6h at this temperature;
(4) reaction is diluted with water to 2~3 times of original volume after terminating, and when temperature is not less than 90 DEG C, centrifugal filtration obtains Filtrate;
(5) in filtrate, it is passed through ammonia or adds ammonium sulfate, being cooled to 0~60 DEG C, filtering, washing, obtain after drying Granular purifying agent Burnt ammonium alum crude product;
(6) technical grade Burnt ammonium alum is obtained after Burnt ammonium alum crude product being carried out recrystallization.
The advantage of the present invention is: < the microspheroidal catalytic cracking spent catalyst of 200 μm prepares water purification agent, by stone to utilize particle diameter The granular solids garbage that oiling factory produces carries out processing utilization, has obtained the water purification agent that can be used for purifying sewage, has solved The fixed-end forces problem of puzzlement petroleum chemical enterprise, it is to avoid its graininess solid waste is to soil and the pollution of air.
Accompanying drawing explanation
Fig. 1 is the mass analysis data of gained water purification agent product in each embodiment;
Fig. 2 is the water purification experiment effect data of gained water purification agent product in each embodiment.
Detailed description of the invention
Embodiment 1
The preparation flow of water purification agent is as follows:
(1) < it is pulled an oar together with water by the microspheroidal catalytic cracking spent catalyst of 200 μm, stirs to weigh 100g particle diameter Mix 30min;
(2) being 20% according to acid concentration in course of reaction, solid-to-liquid ratio is that the ratio of 1:6 adds sulphuric acid, for safety may be used Control acid adding speed;
(3) regulating reaction temperature after acid adding is 140 DEG C, reacts 4h at this temperature;
(4) reaction is diluted with water to 2 times of original volume after terminating, and centrifugal filtration while hot obtains filtrate;
(5) in filtrate, it is passed through ammonia, is cooled to 10 DEG C, filter, washing, obtain water purifying granular agent aluminum sulfate after drying Ammonium crude product;
(6) technical grade water purification agent Burnt ammonium alum is obtained after Burnt ammonium alum crude product being carried out recrystallization.
In the present embodiment, the mass analysis data of water purification agent is shown in Fig. 1, the water purification effect of gained water purification agent sample in the present embodiment Fruit sees Fig. 2.
Embodiment 2
The preparation flow of water purification agent is as follows:
(1) < it is pulled an oar together with water by the microspheroidal catalytic cracking spent catalyst of 40 μm, stirring to weigh 100g particle diameter 30min;
(2) being 30% according to acid concentration in course of reaction, solid-to-liquid ratio is that the ratio of 1:5 adds sulphuric acid, for the sake of peace safety Acid adding speed can be controlled;
(3) regulating reaction temperature after acid adding is 130 DEG C, reacts 4h at this temperature;
(4) reaction is diluted with water to 2 times of original volume after terminating, and centrifugal filtration while hot obtains filtrate;
(5) in filtrate, it is passed through ammonia, is cooled to 50 DEG C, filter, washing, obtain water purifying granular agent aluminum sulfate after drying Ammonium crude product;
(6) technical grade water purification agent Burnt ammonium alum is obtained after Burnt ammonium alum crude product being carried out recrystallization.
In the present embodiment, the mass analysis data of water purification agent is shown in Fig. 1, the water purification effect of gained water purification agent sample in the present embodiment Fruit sees Fig. 2.
Embodiment 3
The preparation flow of water purification agent is as follows:
(1) < it is pulled an oar together with water by the microspheroidal catalytic cracking spent catalyst of 20 μm, stirring to weigh 100g particle diameter 30min;
(2) being 40% according to acid concentration in course of reaction, solid-to-liquid ratio is that the ratio of 1:4 adds sulphuric acid, for the sake of peace safety Acid adding speed can be controlled;
(3) regulating reaction temperature after acid adding is 140 DEG C, reacts 4h at this temperature;
(4) reaction is diluted with water to 2 times of original volume after terminating, and centrifugal filtration while hot obtains filtrate;
(5) in filtrate, it is passed through ammonia, is cooled to 20 DEG C, filter, washing, obtain water purifying granular agent aluminum sulfate after drying Ammonium crude product;
(6) technical grade water purification agent Burnt ammonium alum is obtained after Burnt ammonium alum crude product being carried out recrystallization.
In the present embodiment, the mass analysis data of water purification agent is shown in Fig. 1, the water purification effect of gained water purification agent sample in the present embodiment Fruit sees Fig. 2.
Embodiment 4
The preparation flow of water purification agent is as follows:
(1) < it is pulled an oar together with water by the microspheroidal catalytic cracking spent catalyst of 150 μm, stirs to weigh 100g particle diameter Mix 30min;
(2) being 50% according to acid concentration in course of reaction, solid-to-liquid ratio is that the ratio of 1:3 adds sulphuric acid, for the sake of peace safety Acid adding speed can be controlled;
(3) regulating reaction temperature after acid adding is 130 DEG C, reacts 3h at this temperature;
(4) reaction is diluted with water to 3 times of original volume after terminating, and centrifugal filtration while hot obtains filtrate;
(5) in filtrate, it is passed through ammonia, is cooled to 10 DEG C, filter, washing, obtain water purifying granular agent aluminum sulfate after drying Ammonium crude product;
(6) technical grade water purification agent Burnt ammonium alum is obtained after Burnt ammonium alum crude product being carried out recrystallization.
In the present embodiment, the mass analysis data of water purification agent is shown in Fig. 1, the water purification effect of gained water purification agent sample in the present embodiment Fruit sees Fig. 2.
Embodiment 5
The preparation flow of water purification agent is as follows:
(1) < it is pulled an oar together with water by the microspheroidal catalytic cracking spent catalyst of 200 μm, stirs to weigh 100g particle diameter Mix 30min;
(2) being 60% according to acid concentration in course of reaction, solid-to-liquid ratio is that the ratio of 1:3 adds sulphuric acid, for the sake of peace safety Acid adding speed can be controlled;
(3) regulating reaction temperature after acid adding is 140 DEG C, reacts 3h at this temperature;
(4) reaction is diluted with water to 3 times of original volume after terminating, and centrifugal filtration while hot obtains filtrate;
(5) in filtrate, it is passed through ammonia, is cooled to 30 DEG C, filter, washing, obtain water purifying granular agent aluminum sulfate after drying Ammonium crude product;
(6) technical grade water purification agent Burnt ammonium alum is obtained after Burnt ammonium alum crude product being carried out recrystallization.
In the present embodiment, the mass analysis data of water purification agent is shown in Fig. 1, the water purification effect of gained water purification agent sample in the present embodiment Fruit sees Fig. 2.

Claims (4)

1. water purification agent and preparation method thereof, it is characterised in that concrete operation step is:
(1) by particle diameter, < the microspheroidal catalytic cracking spent catalyst of 200 μm pulls an oar together with water, stir and obtain solidliquid mixture;
(2) sulphuric acid is joined in the solidliquid mixture in (1) carry out dissolve reaction;
(3) reaction is diluted with water to 2~3 times of original volume after terminating, and at a temperature of being not less than 90 DEG C, centrifugal filtration obtains filtrate;
(4) in filtrate, it is passed through ammonia or adds ammonium sulfate, carrying out after being cooled to 0~60 DEG C filtering, washing, the filter cake that will obtain Obtain water purifying granular agent Burnt ammonium alum crude product after drying;
(5) technical grade Burnt ammonium alum is obtained after Burnt ammonium alum crude product being carried out recrystallization.
2., according to described in claim 1, the solid-to-liquid ratio of the solidliquid mixture described in step (1) is 1:2~6.
3., according to described in claim 1, preferably in step (2), cool the filtrate to 0~30 DEG C.
4., according to described in claim 1, the recrystallization condition described in step (5) is: Burnt ammonium alum: water=1:1;Dissolve Temperature is 102 DEG C, and recrystallization temperature is 0~10 DEG C.
CN201610497458.1A 2016-06-29 2016-06-29 A kind of water purification agent and preparation method thereof Pending CN106145172A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107055583A (en) * 2017-05-02 2017-08-18 常熟理工学院 The method that ammonia-alum is prepared by raw material of dead catalyst
CN108328638A (en) * 2018-03-26 2018-07-27 武汉理工大学 A method of preparing alum from FCC dead catalyst

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1673094A (en) * 2005-02-01 2005-09-28 山东师范大学 Synthesis process of nano zinc oxide material
CN1887720A (en) * 2006-07-26 2007-01-03 中国科学院上海硅酸盐研究所 Prepn process of nanometer Zinc oxide powder
CN102531037A (en) * 2012-01-16 2012-07-04 沭阳县飞宏金属新材料有限公司 Chemical preparation method of nanoscale zinc oxide powder
CN104445362A (en) * 2014-11-03 2015-03-25 苏州市泽镁新材料科技有限公司 Preparation method of nano zinc carbonate
CN105236467A (en) * 2014-08-01 2016-01-13 阜阳师范学院 Mass preparation process of nano-grade zinc oxide, and application of nano-grade zinc oxide

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1673094A (en) * 2005-02-01 2005-09-28 山东师范大学 Synthesis process of nano zinc oxide material
CN1887720A (en) * 2006-07-26 2007-01-03 中国科学院上海硅酸盐研究所 Prepn process of nanometer Zinc oxide powder
CN102531037A (en) * 2012-01-16 2012-07-04 沭阳县飞宏金属新材料有限公司 Chemical preparation method of nanoscale zinc oxide powder
CN105236467A (en) * 2014-08-01 2016-01-13 阜阳师范学院 Mass preparation process of nano-grade zinc oxide, and application of nano-grade zinc oxide
CN104445362A (en) * 2014-11-03 2015-03-25 苏州市泽镁新材料科技有限公司 Preparation method of nano zinc carbonate

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
张鹏等: "以工业废催化剂为原料制备超细氢氧化铝的探索", 《科技创新导报》 *
李君: "《炼油装置操作与控制》", 31 March 2011 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107055583A (en) * 2017-05-02 2017-08-18 常熟理工学院 The method that ammonia-alum is prepared by raw material of dead catalyst
CN108328638A (en) * 2018-03-26 2018-07-27 武汉理工大学 A method of preparing alum from FCC dead catalyst

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Application publication date: 20161123

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