CN101200362A - A kind of preparation method of granular packing of biological aerated filter - Google Patents
A kind of preparation method of granular packing of biological aerated filter Download PDFInfo
- Publication number
- CN101200362A CN101200362A CNA2007101156498A CN200710115649A CN101200362A CN 101200362 A CN101200362 A CN 101200362A CN A2007101156498 A CNA2007101156498 A CN A2007101156498A CN 200710115649 A CN200710115649 A CN 200710115649A CN 101200362 A CN101200362 A CN 101200362A
- Authority
- CN
- China
- Prior art keywords
- blast furnace
- furnace slag
- biological aerated
- aerated filter
- filler
- 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.)
- Granted
Links
- 238000002360 preparation method Methods 0.000 title claims description 15
- 238000012856 packing Methods 0.000 title abstract description 6
- 239000002893 slag Substances 0.000 claims abstract description 53
- 239000000945 filler Substances 0.000 claims abstract description 46
- 238000000034 method Methods 0.000 claims abstract description 19
- 239000002994 raw material Substances 0.000 claims abstract description 15
- 239000004568 cement Substances 0.000 claims abstract description 14
- 239000003292 glue Substances 0.000 claims abstract description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 27
- 239000000203 mixture Substances 0.000 claims description 13
- 239000002245 particle Substances 0.000 claims description 13
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 12
- 239000012798 spherical particle Substances 0.000 claims description 10
- 229910052742 iron Inorganic materials 0.000 claims description 6
- 238000003756 stirring Methods 0.000 claims description 6
- 238000012545 processing Methods 0.000 claims description 3
- 238000011156 evaluation Methods 0.000 claims description 2
- 238000009991 scouring Methods 0.000 claims 1
- 238000004519 manufacturing process Methods 0.000 abstract description 16
- 230000008569 process Effects 0.000 abstract description 10
- 230000008901 benefit Effects 0.000 abstract description 7
- 239000002699 waste material Substances 0.000 abstract description 5
- 238000004064 recycling Methods 0.000 abstract description 2
- 244000005700 microbiome Species 0.000 abstract 1
- 238000001179 sorption measurement Methods 0.000 abstract 1
- 230000004083 survival effect Effects 0.000 abstract 1
- 239000003337 fertilizer Substances 0.000 description 8
- 239000002440 industrial waste Substances 0.000 description 8
- XUIMIQQOPSSXEZ-UHFFFAOYSA-N Silicon Chemical compound [Si] XUIMIQQOPSSXEZ-UHFFFAOYSA-N 0.000 description 7
- 229910052710 silicon Inorganic materials 0.000 description 7
- 239000010703 silicon Substances 0.000 description 7
- 239000004567 concrete Substances 0.000 description 6
- 239000004927 clay Substances 0.000 description 4
- 239000002241 glass-ceramic Substances 0.000 description 4
- 230000007613 environmental effect Effects 0.000 description 3
- 230000003628 erosive effect Effects 0.000 description 3
- 239000000843 powder Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 239000012190 activator Substances 0.000 description 2
- 239000011230 binding agent Substances 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- 238000000576 coating method Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000004615 ingredient Substances 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 238000010791 quenching Methods 0.000 description 2
- 230000000171 quenching effect Effects 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 1
- 229910000677 High-carbon steel Inorganic materials 0.000 description 1
- BPQQTUXANYXVAA-UHFFFAOYSA-N Orthosilicate Chemical compound [O-][Si]([O-])([O-])[O-] BPQQTUXANYXVAA-UHFFFAOYSA-N 0.000 description 1
- 240000007594 Oryza sativa Species 0.000 description 1
- 235000007164 Oryza sativa Nutrition 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- 229910004298 SiO 2 Inorganic materials 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 238000005054 agglomeration Methods 0.000 description 1
- 230000002776 aggregation Effects 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 235000013405 beer Nutrition 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000004566 building material Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000003203 everyday effect Effects 0.000 description 1
- 238000010304 firing Methods 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 239000004574 high-performance concrete Substances 0.000 description 1
- 230000036571 hydration Effects 0.000 description 1
- 238000006703 hydration reaction Methods 0.000 description 1
- 229910010272 inorganic material Inorganic materials 0.000 description 1
- 239000011147 inorganic material Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 238000005272 metallurgy Methods 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 230000003334 potential effect Effects 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 235000009566 rice Nutrition 0.000 description 1
- 238000013341 scale-up Methods 0.000 description 1
- 238000012216 screening Methods 0.000 description 1
- 229910052814 silicon oxide Inorganic materials 0.000 description 1
- 238000005245 sintering Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Landscapes
- Curing Cements, Concrete, And Artificial Stone (AREA)
- Biological Treatment Of Waste Water (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
本发明公开了一种曝气生物滤池颗粒填料的制备方法,以高炉水渣为主要原料配以水泥和801胶制备颗粒填料。本发明方法制备的产品具有比表面积大、孔隙率高的特点,极适合微生物的吸附和生存。本发明为高炉水渣资源化探索出一条新途径,同时也为填料生产提供了一条廉价的工艺路线,达到了以废治废的目的,取得了良好的社会效益和经济效益。
The invention discloses a method for preparing granular packing for an aerated biological filter. Blast furnace slag is used as the main raw material and cement and 801 glue are used to prepare the granular packing. The product prepared by the method of the invention has the characteristics of large specific surface area and high porosity, and is very suitable for the adsorption and survival of microorganisms. The invention explores a new way for recycling blast furnace slag, and also provides a cheap process route for filler production, achieves the purpose of treating waste with waste, and obtains good social and economic benefits.
Description
技术领域technical field
本发明涉及一种颗粒填料的生产方法,尤其涉及一种利用工业废物高炉水渣为主要原料制备新型曝气生物滤池颗粒填料方法。The invention relates to a production method of granular packing, in particular to a method for preparing a new type of granular packing for aerated biological filter by using industrial waste blast furnace slag as the main raw material.
背景技术Background technique
本发明所涉及的技术主要包括高炉水渣应用、陶粒填料制备等技术。现有技术介绍如下:The technology involved in the invention mainly includes technologies such as blast furnace slag application and ceramsite filler preparation. The prior art is introduced as follows:
1.高炉水渣1. Blast furnace slag
高炉水渣是炼铁过程中产生的,当它浮在铁水层上面并以高温熔融状态流出时,水淬急冷而成的一种粒化废渣,俗称“水渣”。现阶段对高炉水渣的应用主要集中在以下几个方面:Blast furnace slag is produced during the ironmaking process. When it floats on the molten iron layer and flows out in a high-temperature molten state, it is a kind of granulated waste slag formed by water quenching and quenching, commonly known as "water slag". At present, the application of blast furnace slag mainly focuses on the following aspects:
(1)生产建材(1) Production of building materials
1)生产水泥1) Production of cement
高炉水渣经水淬急冷,来不及形成矿物结晶而把其中的化学能储存于形成的玻璃体中,具有较高的潜在活性,当磨细以后,在水泥熟料矿物的水化产物、石灰、石膏等激发剂作用下,它与水作用可生成水化硅酸盐等水化产物。After the blast furnace slag is quenched and quenched by water, the chemical energy in it is stored in the formed glass body before it can form mineral crystals, which has high potential activity. Under the action of other activators, it reacts with water to generate hydration products such as hydrated silicate.
2)水渣微粉用于混凝土2) Water slag powder is used in concrete
矿渣微粉是将高炉水渣磨细至一定细度的粉体材料,用于水泥的混合材料和混凝土的掺合料。高炉水渣微粉作为混凝土的掺合料,不仅能取代等量的水泥,具有良好的经济效益,而且能显著提高混凝土的技术性能,是国际公认的生产高性能混凝土的主要组分之一。Slag micropowder is a powder material that grinds blast furnace slag to a certain fineness, and is used as a mixture of cement and admixture of concrete. As a concrete admixture, blast furnace slag powder can not only replace the same amount of cement, which has good economic benefits, but also can significantly improve the technical performance of concrete. It is internationally recognized as one of the main components for the production of high-performance concrete.
由于矿渣微粉作为混凝土的掺合料有良好的技术效益和经济效益,近年来,我国一些大城市的建筑工程应用矿渣微粉混凝土已经逐步展开,发展前景良好。Because slag micropowder has good technical and economic benefits as a concrete admixture, in recent years, the application of slag micropowder concrete in construction projects in some large cities in my country has gradually started, and the development prospect is good.
(2)生产硅肥(2) Production of silicon fertilizer
硅肥是一种以含氧化硅(SiO2)和氧化钙(CaO)为主的矿物质肥料,它是水稻等农作物生长不可缺少的营养元素之一。硅肥现被国际土壤学界确认为继氮(N)、磷(P)、钾(K)之后第四大元素肥料。生产硅肥的主要原材料为高炉水渣。Silicon fertilizer is a mineral fertilizer mainly containing silicon oxide (SiO 2 ) and calcium oxide (CaO). It is one of the indispensable nutrients for the growth of rice and other crops. Silicon fertilizer is now recognized by the international soil science community as the fourth largest element fertilizer after nitrogen (N), phosphorus (P) and potassium (K). The main raw material for producing silicon fertilizer is blast furnace slag.
硅肥的加工过程为:把水渣磨细,细度为80目~100目,添入适量硅元素活化剂,搅拌混合后装袋(或搅拌混合造粒后装袋),硅肥的工业化生产比较简单。The processing process of silicon fertilizer is as follows: grind water slag finely, with a fineness of 80 mesh to 100 mesh, add an appropriate amount of silicon element activator, stir and mix and then bag (or stir and mix and granulate and then bag), the industrialization of silicon fertilizer Production is relatively simple.
(3)生产微晶玻璃(3) Production of glass-ceramic
微晶玻璃是近几十年发展起来的一种用途很广的新型无机材料。高炉水渣微晶玻璃产品,比高碳钢硬,比铝轻,其机械性能比普通玻璃好,耐磨性不亚于铸石,热稳定性好,电绝缘性能与高频瓷接近,矿渣微晶玻璃用于冶金、化工、煤炭、机械等工业部门的各种容器设备的防腐层和金属表面的耐磨层以及制造管材等,使用效果很好。Glass-ceramics is a new type of inorganic material that has been developed in recent decades and has a wide range of uses. Blast furnace slag glass-ceramic products are harder than high-carbon steel and lighter than aluminum. Glass-ceramic is used in metallurgy, chemical industry, coal, machinery and other industrial sectors for anti-corrosion coatings of various container equipment and wear-resistant coatings on metal surfaces, as well as in the manufacture of pipes, etc., with good results.
2.陶粒填料2. Ceramsite filler
陶粒填料是采用优质粘土为原料,经团粒、高温烧制、筛分等一系列工艺加工而成的水处理填料。普通的陶粒填料的原料主要是粘土、页岩等,需要进行采挖,并且在制作时通常需要进行烧结,需要耗费很多的煤炭资源,这在当今能源紧缺的情况下势必造成其制作成本的增加。Ceramsite filler is a water treatment filler that uses high-quality clay as raw material and is processed by a series of processes such as agglomeration, high-temperature firing, and screening. Ordinary ceramsite fillers are mainly made of clay, shale, etc., which need to be excavated, and usually need to be sintered during production, which consumes a lot of coal resources, which will inevitably lead to its production cost under the current energy shortage situation. Increase.
高炉水渣颗粒填料同普通的陶粒填料的生产过程的区别主要在于原料的不同。普通陶粒填料的原料主要是粘土、页岩等,而高炉水渣颗粒填料的主要原料高炉水渣为工业废物,相对于粘土和页岩来说,高炉水渣的原料成本较低,因此,高炉水渣颗粒填料相对于普通陶粒填料在成本方面有很大优势。The difference between the production process of blast furnace slag particle filler and ordinary ceramsite filler mainly lies in the difference of raw materials. The raw materials of ordinary ceramsite filler are mainly clay, shale, etc., while the main raw material of blast furnace slag granular filler is industrial waste. Compared with clay and shale, the raw material cost of blast furnace slag is lower. Therefore, Compared with ordinary ceramsite filler, blast furnace slag particle filler has great advantages in cost.
关于高炉水渣颗粒填料的制作特别是使用粘结剂将高炉水渣进行粘结的应用和研究,经检索,还未见相关报道。There is no relevant report about the production of blast furnace slag particle filler, especially the application and research of using binder to bond blast furnace slag.
发明内容Contents of the invention
针对现有技术的不足,本发明的目的在于提供一种利用工业废物高炉水渣为主要原料制备新型曝气生物滤池颗粒填料方法。Aiming at the deficiencies of the prior art, the object of the present invention is to provide a method for preparing a novel biological aerated filter granular filler using industrial waste blast furnace slag as the main raw material.
本发明所述曝气生物滤池颗粒填料的制备方法,步骤如下:The preparation method of the biological aerated filter particle filler of the present invention, the steps are as follows:
(1)原料选取及处理:取高炉水渣,用水冲洗,并除去其中的大块杂物,然后风干,之后用球磨机进行破碎,过20目的标准筛,筛分后的高炉水渣备用;(1) Raw material selection and processing: take the blast furnace slag, wash it with water, and remove the large debris therein, then air-dry it, then crush it with a ball mill, pass through a 20-mesh standard sieve, and use the sieved blast furnace slag for later use;
(2)配料:称取步骤(1)制得的高炉水渣,加入其质量百分比为4%~20%的水泥和其质量百分比为4%~20%的801胶,充分搅拌混合均匀;(2) Batching: take the blast furnace slag obtained in step (1), add its mass percentage as 4% to 20% cement and its mass percentage as 4% to 20% 801 glue, fully stir and mix;
(3)成球:将步骤(2)制取的混合物制成直径为3~6mm的球形颗粒;(3) into balls: making the mixture prepared in step (2) into spherical particles with a diameter of 3 to 6 mm;
(4)养护:将步骤(3)制取的球形颗粒每天撒水6~12次,养护3~6天,即得曝气生物滤池颗粒填料成品——高炉水渣颗粒填料。(4) Curing: Sprinkle the spherical particles produced in step (3) with water 6 to 12 times a day, and cure for 3 to 6 days to obtain the finished product of granular filler for biological aerated filter—blast furnace slag granular filler.
上述曝气生物滤池颗粒填料的制备方法中:步骤(1)所述杂物是主要指废铁块。In the preparation method of the granular filler for the biological aerated filter mentioned above: the sundries mentioned in the step (1) mainly refer to scrap iron pieces.
上述曝气生物滤池颗粒填料的制备方法中:步骤(2)所述水泥质量百分比优选5%~15%,801胶质量百分比优选5%~12%。In the preparation method of the granular filler for the biological aerated filter: the mass percentage of cement in step (2) is preferably 5%-15%, and the mass percentage of 801 glue is preferably 5%-12%.
其中:步骤(2)所述水泥质量百分比最优选为10%,801胶质量百分比最优选为6%。Wherein: the most preferred mass percentage of cement in step (2) is 10%, and the most preferred mass percentage of 801 glue is 6%.
上述曝气生物滤池颗粒填料的制备方法中:步骤(4)所述养护时间优选3~5天,每天撒水次数优选6~10次。In the preparation method of the granular filler for the biological aerated filter: the curing time in step (4) is preferably 3-5 days, and the number of sprinkling water is preferably 6-10 times per day.
其中:步骤(4)所述养护时间最优选是3天,每天撒水次数最优选是6次。Wherein: the curing time described in step (4) is most preferably 3 days, and the number of sprinkling water every day is most preferably 6 times.
上述曝气生物滤池颗粒填料的制备方法中:步骤(4)所述高炉水渣颗粒填料以测其密度、水冲刷损失率作为评价指标,采用100/(密度×水冲刷损失率(0.2MPa压力下))作为综合指标考察填料性质。In the preparation method of the above-mentioned biological aerated filter particle filler: the blast furnace slag particle filler described in step (4) is to measure its density and water scour loss rate as evaluation index, adopt 100/(density × water scour loss rate (0.2MPa Under pressure)) as a comprehensive index to investigate the properties of fillers.
上述的曝气生物滤池颗粒填料的制备方法中:颗粒填料的制备在放大生产中,高炉水渣、水泥、801胶用量遵照原比例关系量放大执行。In the preparation method of the granular filler of the above-mentioned biological aerated filter: the preparation of the granular filler is in the scale-up production, and the amount of blast furnace slag, cement, and 801 glue is scaled up according to the original proportional relationship.
本发明的曝气生物滤池颗粒填料制备方法具有工艺创新、方法简便、成本低廉、利于环保护等突出优点,生产出的产品为直径3~6mm的球形颗粒,颗粒平均填料比表面积为4.0~5.0m2/g、平均抗压强度为5.8MPa。产品比表面积大、孔隙率高,是一种优良的生物滤池填料,经济效益、社会效益、环境效益显著。The preparation method of granular packing for biological aerated filter of the present invention has outstanding advantages such as technological innovation, simple and convenient method, low cost, and being beneficial to environmental protection. 5.0m 2 /g, and the average compressive strength is 5.8MPa. The product has a large specific surface area and high porosity, and is an excellent biological filter filler with remarkable economic, social and environmental benefits.
本发明与现有技术相比所具备的优点在于:Compared with the prior art, the present invention has the following advantages:
(1)利用工业废物为原料,可大大降低曝气生物滤池颗粒填料的生产成本和废水处理成本,有利于该新型填料的推广应用;(1) Using industrial waste as raw material can greatly reduce the production cost and wastewater treatment cost of biological aerated filter granular filler, which is conducive to the popularization and application of this new filler;
(2)用本发明方法制备的产品作为曝气生物滤池的填料来处理啤酒废水,试验结果表明:COD去除率可达到80%,NH4 +-N去除率可达到90%,说明本产品具有较高的应用价值;(2) The product prepared by the inventive method is used as the filler of the biological aerated filter to process beer wastewater, and the test results show that the COD removal rate can reach 80%, and the NH 4 + -N removal rate can reach 90%, indicating that this product Has high application value;
(3)对工业固体废物进行综合利用,在降低曝气生物滤池颗粒填料生产成本的同时,又能提高其环境价值,达到以废治废的目的,实现固体实物的资源化,为工业废物高炉水渣的回收利用探索出一条新途径;(3) The comprehensive utilization of industrial solid waste can not only reduce the production cost of biological aerated filter granular filler, but also improve its environmental value, achieve the purpose of treating waste with waste, realize the resource utilization of solid objects, and provide industrial waste A new way has been explored for the recycling of blast furnace slag;
(4)合成过程中不需烧结,只使用粘结剂粘结,实现了节能降耗,操作简单,投资省,见效快,有明显的实用价值。(4) No sintering is required in the synthesis process, only a binder is used for bonding, which realizes energy saving and consumption reduction, simple operation, low investment, quick effect, and obvious practical value.
附图说明Description of drawings
图1为本发明的合成工艺流程图。Fig. 1 is a synthetic process flow chart of the present invention.
具体实施方式Detailed ways
下面结合附图对本发明进行详细说明。The present invention will be described in detail below in conjunction with the accompanying drawings.
实施例1Example 1
如图1所示,利用工业废物高炉水渣制备曝气生物滤池颗粒填料包括以下步骤:As shown in Figure 1, the use of industrial waste blast furnace slag to prepare granular fillers for biological aerated filters includes the following steps:
(1)原料选取及处理:取高炉水渣,用水冲洗,并除去其中的大块杂物(主要是废铁块),然后风干,之后采用球磨机进行破碎,过20目的标准筛,筛分后获得的高炉水渣备用。(1) Raw material selection and treatment: take blast furnace slag, wash it with water, and remove large pieces of debris (mainly scrap iron), then air-dry, and then use a ball mill to crush it, pass through a 20-mesh standard sieve, and sieve The obtained blast furnace slag is used for future use.
(2)配料:称取步骤(1)制得高炉水渣700g,加入其质量百分比为8%的水泥和其质量百分比为4%的801胶,充分混合,搅拌均匀。(2) Batching: Weigh 700 g of the blast furnace slag obtained in step (1), add 8% cement and 4% 801 glue by mass, mix thoroughly and evenly.
(3)成球:将步骤(2)制取的混合物加工成直径为3~6mm的球形颗粒。(3) Balling: process the mixture prepared in step (2) into spherical particles with a diameter of 3-6 mm.
(4)养护:将步骤(3)制取的球形颗粒每天撒水6次,养护3天后,即得高炉水渣颗粒填料成品,测得其密度为2.55g/m3,水冲刷损失率为1.6%。(4) Curing: Sprinkle the spherical particles prepared in step (3) with water 6 times a day, and after curing for 3 days, the finished product of blast furnace slag particle filler is obtained. The measured density is 2.55g/m 3 , and the water erosion loss rate is 1.6 %.
实施例2Example 2
如图1所示,利用工业废物高炉水渣制备曝气生物滤池颗粒填料包括以下步骤:As shown in Figure 1, the use of industrial waste blast furnace slag to prepare granular fillers for biological aerated filters includes the following steps:
(1)原料选取及处理:取高炉水渣,用水冲洗,并除去其中的大块杂物(主要是废铁块),然后风干,之后采用球磨机进行破碎,过20目的标准筛,筛分后获得的高炉水渣备用。(1) Raw material selection and treatment: take blast furnace slag, wash it with water, and remove large pieces of debris (mainly scrap iron), then air-dry, and then use a ball mill to crush it, pass through a 20-mesh standard sieve, and sieve The obtained blast furnace slag is used for future use.
(2)配料:称取步骤(1)制得高炉水渣700g,加入其质量百分比为12%的水泥和其质量百分比为8%的801胶,充分混合,搅拌均匀。(2) Ingredients: Weigh 700 g of the blast furnace slag obtained in step (1), add 12% cement and 8% 801 glue by mass, fully mix and evenly stir.
(3)成球:将步骤(2)制取的混合物加工成直径为3~6mm的球形颗粒。(3) Balling: process the mixture prepared in step (2) into spherical particles with a diameter of 3-6 mm.
(4)养护:将步骤(3)制取的球形颗粒每天撒水7次,养护3天后即得高炉水渣颗粒填料成品,测得其密度为2.83g/m3,水冲刷损失率为1.1%。(4) Curing: Sprinkle the spherical particles produced in step (3) with water 7 times a day, and after 3 days of curing, the finished product of blast furnace slag particle filler is obtained. The measured density is 2.83g/m 3 , and the water erosion loss rate is 1.1%. .
实施例3Example 3
如图1所示,利用工业废物高炉水渣制备曝气生物滤池颗粒填料包括以下步骤:As shown in Figure 1, the use of industrial waste blast furnace slag to prepare granular fillers for biological aerated filters includes the following steps:
(1)原料选取及处理:取高炉水渣,用水冲洗,并除去其中的大块杂物(主要是废铁块),然后风干,之后采用球磨机进行破碎,过20目的标准筛,筛分后获得的高炉水渣备用。(1) Raw material selection and treatment: take blast furnace slag, wash it with water, and remove large pieces of debris (mainly scrap iron), then air-dry, and then use a ball mill to crush it, pass through a 20-mesh standard sieve, and sieve The obtained blast furnace slag is used for future use.
(2)配料:称取步骤(1)制得高炉水渣700g,加入质量百分比为10%的水泥和其质量百分比为6%的801胶,充分混合,搅拌均匀。(2) Ingredients: Weigh 700 g of blast furnace slag obtained in step (1), add 10% cement by mass percentage and 6% 801 glue by mass percentage, fully mix, and stir evenly.
(3)成球:将步骤(2)制取的混合物加工成直径为3~6mm的球形颗粒。(3) Balling: process the mixture prepared in step (2) into spherical particles with a diameter of 3-6 mm.
(4)养护:将步骤(3)制取的球形颗粒每天撒水8次,养护4天后即得高炉水渣颗粒填料成品,测得其密度为2.95g/m3,水冲刷损失率为1.3%。(4) Curing: Sprinkle the spherical particles prepared in step (3) with water 8 times a day, and after curing for 4 days, the finished product of blast furnace slag particle filler is obtained. The measured density is 2.95g/m 3 , and the water erosion loss rate is 1.3%. .
Claims (7)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB2007101156498A CN100556848C (en) | 2007-12-19 | 2007-12-19 | A kind of preparation method of granular packing of biological aerated filter |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB2007101156498A CN100556848C (en) | 2007-12-19 | 2007-12-19 | A kind of preparation method of granular packing of biological aerated filter |
Publications (2)
Publication Number | Publication Date |
---|---|
CN101200362A true CN101200362A (en) | 2008-06-18 |
CN100556848C CN100556848C (en) | 2009-11-04 |
Family
ID=39515762
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CNB2007101156498A Expired - Fee Related CN100556848C (en) | 2007-12-19 | 2007-12-19 | A kind of preparation method of granular packing of biological aerated filter |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN100556848C (en) |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101318737B (en) * | 2008-07-10 | 2010-12-01 | 济南大学 | A non-burning porous water slag filter material and its preparation method |
CN102079572A (en) * | 2010-12-16 | 2011-06-01 | 江苏高淳陶瓷股份有限公司 | Preparation and application method of biofilm honeycomb ceramic carrier with low cost |
CN102557550A (en) * | 2012-03-14 | 2012-07-11 | 山东大学 | Biological aerated filter filler prepared by use of construction wastes, and preparation method thereof |
CN103395907A (en) * | 2013-08-20 | 2013-11-20 | 陈双喜 | Method of filtering oil stains by adopting waterproof and ventilating sands |
CN108408881A (en) * | 2018-03-19 | 2018-08-17 | 包头钢铁(集团)有限责任公司 | It is a kind of using metallurgical solid waste as the biological aerated filter of filtrate |
-
2007
- 2007-12-19 CN CNB2007101156498A patent/CN100556848C/en not_active Expired - Fee Related
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101318737B (en) * | 2008-07-10 | 2010-12-01 | 济南大学 | A non-burning porous water slag filter material and its preparation method |
CN102079572A (en) * | 2010-12-16 | 2011-06-01 | 江苏高淳陶瓷股份有限公司 | Preparation and application method of biofilm honeycomb ceramic carrier with low cost |
CN102079572B (en) * | 2010-12-16 | 2012-10-03 | 江苏高淳陶瓷股份有限公司 | Preparation and application method of biofilm honeycomb ceramic carrier with low cost |
CN102557550A (en) * | 2012-03-14 | 2012-07-11 | 山东大学 | Biological aerated filter filler prepared by use of construction wastes, and preparation method thereof |
CN102557550B (en) * | 2012-03-14 | 2013-03-06 | 山东大学 | Biological aerated filter filler prepared by use of construction wastes, and preparation method thereof |
CN103395907A (en) * | 2013-08-20 | 2013-11-20 | 陈双喜 | Method of filtering oil stains by adopting waterproof and ventilating sands |
CN108408881A (en) * | 2018-03-19 | 2018-08-17 | 包头钢铁(集团)有限责任公司 | It is a kind of using metallurgical solid waste as the biological aerated filter of filtrate |
Also Published As
Publication number | Publication date |
---|---|
CN100556848C (en) | 2009-11-04 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN104030633B (en) | A kind of nickel dreg concrete | |
CN105645895A (en) | Ferronickel slag ultrahigh-strength concrete and preparation method thereof | |
CN101691291A (en) | Method for producing pasty unclassified tailing filling materials containing red mud | |
CN102329105A (en) | Method for preparing concrete by taking manganese residue-steel residue-limestone powder as admixture | |
CN101348335B (en) | Method for preparing special cement for high-performance concrete from magnetite-quartzite iron tailings | |
CN101215137A (en) | Ferromanganese slag concrete admixture and production method thereof | |
CN101353245B (en) | Waste stone dust-containing high performance superfine sand concrete gel material and use method thereof | |
CN110054442A (en) | A kind of regeneration concrete mixture and its preparation process | |
CN101693186B (en) | Dephosphorization and denitrification integrated material prepared based on battering method and preparation method thereof | |
CN113929321B (en) | An optimized magnesium slag-based cementitious material and its preparation method | |
CN101200362A (en) | A kind of preparation method of granular packing of biological aerated filter | |
CN113213797A (en) | Steel slag and slag composite admixture and preparation method and application thereof | |
CN101654737A (en) | Compound iron ore pellet of molybdenum tailings and sulfate slags and preparation method thereof | |
CN106587675B (en) | A kind of high activity nickel slag base cement mixture and preparation method thereof | |
CN108484062A (en) | A kind of gravity flowing levelling mortar prepared with coal liquifaction gasifier slag | |
AU2021104088A4 (en) | Method for preparing porous lightweight fine aggregate and micropowder from manganese-silicon slag and applications thereof | |
CN104402335A (en) | High-strength concrete employing magnetized reduced roasted iron-beneficiation tailings as admixture | |
CN107500734A (en) | It is a kind of using industrial inorganic hazardous waste and low-grade alumina-silica mineral as ceramic water-permeable brick of raw material and preparation method thereof | |
CN104496222B (en) | The method manufacturing controllability low-intensity material with carbide slag, slag and gangue | |
CN106316421B (en) | Efficient energy-saving magnesium ramming mass prepared by recycling waste magnesium brick material of cement plant and preparation process | |
CN101696092A (en) | Method for manufacturing porous sound absorption material by using blast furnace water quenching slag | |
CN115321897A (en) | Low-carbon cementing material with high early strength and processing method thereof | |
CN103553469B (en) | High titania blast furnace slag mortar double-doped with micro powder | |
CN109111140A (en) | A method of high activity slag micropowder is prepared using citric acid waste | |
CN117658577B (en) | Soft soil curing agent based on garbage incineration secondary bottom slag and preparation method and application thereof |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20091104 Termination date: 20181219 |
|
CF01 | Termination of patent right due to non-payment of annual fee |