CN1724110A - Process for preparing porous light filtering material using coal gangue as raw material - Google Patents

Process for preparing porous light filtering material using coal gangue as raw material Download PDF

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Publication number
CN1724110A
CN1724110A CN200510040291.8A CN200510040291A CN1724110A CN 1724110 A CN1724110 A CN 1724110A CN 200510040291 A CN200510040291 A CN 200510040291A CN 1724110 A CN1724110 A CN 1724110A
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China
Prior art keywords
minute
gangue
raw material
time
sintering
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Pending
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CN200510040291.8A
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Chinese (zh)
Inventor
张文艺
翟建平
李琴
黎飞虎
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Nanjing University
Anhui University of Technology AHUT
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Nanjing University
Anhui University of Technology AHUT
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Priority to CN200510040291.8A priority Critical patent/CN1724110A/en
Publication of CN1724110A publication Critical patent/CN1724110A/en
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  • Treatment Of Sludge (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

A process for preparing the light-weight spherical porous filtering material from coal gangue includes such steps as proportionally mixing coal gangue, powdered coal ash, red mud generated by smelting steel and puffing agent, stirring, adding water and shaping agent, granulating, drying, high-temp sintering and natural cooling. Its advantages are no pollution and high properties of product used for treating sewage.

Description

With the gangue is the method for feedstock production spherical porous light filtrate
Technical field:
The invention belongs to technical field of waste water processing, being specifically related to a kind of is primary raw material is produced spherical porous light sewage disposal filtrate through high temperature sintering preparation method with the gangue.
Background technology:
Gangue is the waste rock that gives off in the progress of coal mining, and it is a kind of large industrial solid castoff.China's gangue output is about the 15%-20% of raw coal total output, accumulates to reach 7,000,000,000 t, and still with the speed increment of annual emissions 1.5 hundred million t.And gangue year comprehensive utilization ratio still less than 20%, remaining gangue adopts circular cone type or cheuch Dumpage type to be stacked loosely in naturally around the mine more, has both occupied cultivated land, and again environment is polluted.The comprehensive utilization of the gangue spoil except that calorific value>2000Kcal/kg is used for the generating, and other is usually as repairing the roads, build charges and brickmaking etc.The spoil that can be used in generating only accounts for 5% of total amount, though the making coal gangue brick technology maturation, because of the price of brick is lower, production cost is higher, and added value of product is lower, and commercial value is little, thereby causes a large amount of gangues to pile up.The development and use gangue makes it form high value added product, and is significant.
The sewage disposal biofilter is a kind of aerobe membrane treatment process of apposition growth, and its key is the carrier of biomembrane apposition growth a---filtrate.Filtrate is as microorganism carrier, and the whole process that directly affects microbial growth, breeds and come off influences the water treatment effect.Requirement is to media performance: specific area is big, microorganism colonization is fast, set microbial film amount is many, bioaffinity good, aging biomembrane easily comes off, antiacid alkali, resistance to oxidation, not easily biological-degradable, be difficult for aging, oxygen-transfer efficiency is high, light weight, mechanical strength are big, long service life, low price etc.External filtrate generally adopts the volcanic rock manufacturing, costs an arm and a leg.For example, China introduces Ma Lan river, the Daliang City sewage treatment plant that Germany technology is built, biofilter material 7933m in the mid-90 in 20th century 3, its used filtrate is external import, C.I.F. is 4500 yuan/m 3Thereby, increased construction investment.China's sintering filtrate in the market is mainly with raw material productions such as shale and clays, and behind the one-tenth piece sintering, crushing and screening obtains.Though carrier surface forming biofilm property is good, its shape inequality, intensity difference, easily broken, porosity is little, stop up easily, not water-fast washing away, charge level is uneven after operation a period of time, causes water distribution, gas distribution inhomogeneous, and aeration aerating efficient is low, treatment effect descends.
Summary of the invention:
The invention provides a kind of is primary raw material with the gangue, adds a small amount of swelling agent, prepares light porous sewage disposal filter manufacture method through high temperature sintering.The ball-type filtrate of method manufacturing is specifically designed to water treatment thus.
The concrete preparation process of method provided by the present invention is as follows:
1, the gangue of pulverizing is joined to mix in the mixing kettle by formula ratio and stirred 20-30 minute with flyash, steel-making red mud, the swelling agent of oven dry.
2, mixed raw materials is joined in the tumbling disk granulator, add entry by formula ratio again and forming agent carries out granulation, granularity is controlled at particle diameter 4-8mm, and material time of staying in tumbling disk granulator is 20-40 minute.
3, pellet is joined carry out drying and sintering in the high temperature calcining kiln, baking temperature 300-450 ℃, sintering temperature 1000-1180 ℃, time 60-120 minute, grog is cooling naturally at normal temperatures.
The preferred process conditions of the present invention are: raw material incorporation time 20-30 minute, in the comminutor time of staying 20-40 minute, 60-80 minute drying time in calcining kiln; baking temperature 350-400 ℃; firing time 20-60 minute, sintering temperature 1100-1180 ℃, grog is cooling naturally at normal temperatures.
The raw material proportioning is benchmark with the quality: gangue 65-95%, and flyash 0-25%, steel-making red mud 0-10%, swelling agent 5% adds the liquid molding agent of water and the material quantity 2-3% of material quantity 20-30% in addition.Water and forming agent are mainly used in the powder granulation, are not the compositions of finished product filtrate.Swelling agent in the prescription can be selected any one in waste plastics powder, coke blacking, charcoal powder, carbon black, dicalcium powder, the mica powder, but the present invention recommends to adopt charcoal powder, waste plastics powder and mica powder.Forming agent in the prescription is that concentration is 0.2% polyacrylamide solution.
The light porous spherolite that produces thus can reach the quality requirement as water treatment filter material, and its main physical and chemical parameter is: specific area 6-8.6/m 2/ g, porosity 40-50/%, bulk density 900-1000kg/m 3, wear rate<2%, average pore size 125-210/ μ m.
Spherical light multiporous biological filtrate of the present invention is a primary raw material with gangue, flyash, steel-making red mud, characteristics such as have rough surface, specific area is big, porosity is high, appearance is hard, and is anticorrosive, wear-resistant.Overcome the shortcoming of traditional filtrate better, main performance index such as its carrier surface forming biofilm property, the distribute water and air uniformity, bulk specific weight, intensity, porosity, specific area all are better than other products.Compare with external product, have the very high ratio of performance to price.
Distinguishing feature of the present invention shows as two aspects, and the one, the product that has the environmental protection industry of higher economic worth with the industrial residue for raw material production.Being the big argument discarded object that produces in coal, electric power, the steel and iron industry production process---gangue, flyash and steel-making red mud provide new outlet, make its biological sewage that becomes high added value handle the filtrate raw materials for production, particularly gangue, utilization of coal ash have realized the purpose of " treatment of wastes with processes of wastes against one another ".On the other hand, can produce the filtrate of appointed product aperture and apparent density easily by the granularity and the consumption of control charcoal powder, waste plastics powder or mica powder.
The specific embodiment:
Embodiment 1:
With gangue, flyash, steel-making red mud, charcoal powder is raw material.Proportioning is: gangue 65g, flyash 25g, steel-making red mud 5g, mica powder 5g.Production process is as follows:
1. with feed coal spoil 65g, flyash 25g, steel-making red mud 5g, mica powder 5g, join respectively and mix 20 minutes in the mixing kettle, the water and the 2mL concentration that add 28mL then are that 0.2% polyacrylamide solution mixes the artificial granulation.
2. pellet is put into temperature and is 400 ℃ sintering furnace, insulation oven dry 60 minutes, the sintering that heats up then is expanded.When being warmed up to 1180 ℃, be incubated 8 minutes.
3. after coming out of the stove, the haydite that sinters naturally cools to room temperature.
The difference of embodiment 2,3 and embodiment 1 is that the consumption of flyash reduces, and all the other raw material consumptions are constant, and operating condition is constant.Embodiment 4 increases no flyash with the difference of embodiment 1 for steel-making red mud consumption.Embodiment 5 is that raw material is a gangue with the difference of embodiment 1, does not have flyash and steel-making red mud, and all the other are constant.Embodiment 3 swelling agents change charcoal powder into by mica powder, and embodiment 4 swelling agents change the waste plastics powder into by mica powder, and raw material consumption and operating condition are all constant, and be identical with embodiment 1.The raw material proportioning of embodiment 1-5 sees Table 1, and the physical and chemical index of corresponding product sees Table 2.
The consumption of different material in table 1 example (material quantity 100g)
The embodiment numbering Gangue/g Flyash/g Steel-making red mud/g Swelling agent/g Water/mL Forming agent/mL
1 65 25 5 5 28 2
2 75 15 5 5 28 2
3 85 5 5 5 28 2
4 85 0 10 5 28 2
5 95 0 0 5 28 2
The product physical and chemical index of table 2 different ratios of raw materials examples produce
The embodiment numbering Apparent density/kg/m 3 Bulk density/kg/m 3 Porosity/% Specific area/m 2/g Wear rate/% Average pore size/μ m
1 1.21 0.914 23.8 6.35 <2% 210
2 1.78 0.899 49.5 7.53 <2% 125
3 1.81 0.926 48.1 8.12 <2% 175
4 1.60 0.927 45.1 8.64 <2% 180
5 1.86 1.02 54.8 8.06 <2% 200

Claims (4)

1, a kind of is the method for feedstock production spherical porous light filtrate with the gangue, it is characterized in that it is a primary raw material with gangue, flyash and steel-making red mud, adds a small amount of forming agent, swelling agent, forms through mixing, granulation, drying and high temperature sintering; The quality proportioning of described raw material and each component is: gangue 65-95%, and flyash 0-25%, steel-making red mud 0-10%, swelling agent 5% add the liquid molding agent of water and the material quantity 2-3% of material quantity 20-30% in addition; Concrete preparation process is as follows:
1. the gangue of pulverizing is joined to mix in the mixing kettle by formula ratio and stirred 20-30 minute with flyash, steel-making red mud, the swelling agent of oven dry;
2. mixed raw materials is joined in the tumbling disk granulator, add entry by formula ratio again and forming agent carries out granulation, granularity is controlled at particle diameter 4-8mm, and material time of staying in tumbling disk granulator is 20-40 minute;
3. pellet is joined and carry out drying and sintering in the high temperature calcining kiln, time 60-120 minute, baking temperature 300-450 ℃, sintering temperature 1000-1180 ℃, grog is cooling naturally at normal temperatures.
2,, it is characterized in that described swelling agent is according to the described method of claim 1: in charcoal powder, waste plastics powder and the mica powder any one.
3, according to the described method of claim 1, the described forming agent of its feature is: concentration is 0.2% polyacrylamide solution.
4, according to the described method of claim 1; it is characterized in that its process conditions are: raw material incorporation time 20-30 minute; in the comminutor time of staying 20-40 minute; 60-80 minute drying time in calcining kiln; baking temperature 350-400 ℃; firing time 20-60 minute, sintering temperature 1100-1180 ℃, grog is cooling naturally at normal temperatures.
CN200510040291.8A 2005-05-30 2005-05-30 Process for preparing porous light filtering material using coal gangue as raw material Pending CN1724110A (en)

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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103265190A (en) * 2013-05-04 2013-08-28 滕州市东郭水泥有限公司 Technology and equipment for treating waste water and waste liquid by JT kiln of cement mill
CN104069690A (en) * 2014-04-11 2014-10-01 内蒙古大学 Zeolite ceramisite filter material prepared by gangue and preparation method of zeolite ceramisite filter material
CN104759152A (en) * 2015-03-18 2015-07-08 蚌埠首创滤清器有限公司 Wear-resistant composite filter material prepared by blending melt-blown polypropylene with modified fly ash and used for sewage treatment and preparation method thereof
CN104759146A (en) * 2015-03-18 2015-07-08 蚌埠德美过滤技术有限公司 High-adsorbability composite filter material prepared by blending melt-blown polypropylene with modified attapulgite and used for sewage treatment and preparation method thereof
CN105688507A (en) * 2016-01-28 2016-06-22 沈阳建筑大学 Sintering method of coal gangue modified porous lightweight filtering material
CN105999850A (en) * 2016-07-08 2016-10-12 吴印强 Efficient composite carborundum filter material and preparing method and application thereof
CN107573094A (en) * 2017-09-11 2018-01-12 蒙娜丽莎集团股份有限公司 A kind of micropore ceramic filtration medium for hot environment and preparation method thereof

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103265190A (en) * 2013-05-04 2013-08-28 滕州市东郭水泥有限公司 Technology and equipment for treating waste water and waste liquid by JT kiln of cement mill
CN103265190B (en) * 2013-05-04 2016-03-23 滕州市东郭水泥有限公司 Utilize cement mill JT kiln process waste water and waste liquid Processes and apparatus
CN104069690A (en) * 2014-04-11 2014-10-01 内蒙古大学 Zeolite ceramisite filter material prepared by gangue and preparation method of zeolite ceramisite filter material
CN104069690B (en) * 2014-04-11 2016-06-15 内蒙古大学 A kind of utilize coal gangue to prepare zeolite ceramsite filtrate and its preparation method
CN104759152A (en) * 2015-03-18 2015-07-08 蚌埠首创滤清器有限公司 Wear-resistant composite filter material prepared by blending melt-blown polypropylene with modified fly ash and used for sewage treatment and preparation method thereof
CN104759146A (en) * 2015-03-18 2015-07-08 蚌埠德美过滤技术有限公司 High-adsorbability composite filter material prepared by blending melt-blown polypropylene with modified attapulgite and used for sewage treatment and preparation method thereof
CN105688507A (en) * 2016-01-28 2016-06-22 沈阳建筑大学 Sintering method of coal gangue modified porous lightweight filtering material
CN105999850A (en) * 2016-07-08 2016-10-12 吴印强 Efficient composite carborundum filter material and preparing method and application thereof
CN105999850B (en) * 2016-07-08 2019-01-29 河北银达环保科技有限公司 High efficiency composition Buddha's warrior attendant sand filtering material and its preparation method and application
CN107573094A (en) * 2017-09-11 2018-01-12 蒙娜丽莎集团股份有限公司 A kind of micropore ceramic filtration medium for hot environment and preparation method thereof
CN107573094B (en) * 2017-09-11 2020-04-07 蒙娜丽莎集团股份有限公司 Microporous ceramsite filter medium for high-temperature environment and preparation method thereof

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