CN202322657U - System for firing ceramsite by using sludge - Google Patents
System for firing ceramsite by using sludge Download PDFInfo
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- CN202322657U CN202322657U CN2011203870484U CN201120387048U CN202322657U CN 202322657 U CN202322657 U CN 202322657U CN 2011203870484 U CN2011203870484 U CN 2011203870484U CN 201120387048 U CN201120387048 U CN 201120387048U CN 202322657 U CN202322657 U CN 202322657U
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- sludge
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- rotary kiln
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- firing
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- 239000010802 sludge Substances 0.000 title claims abstract description 40
- 238000010304 firing Methods 0.000 title claims abstract description 8
- 238000005469 granulation Methods 0.000 claims abstract description 7
- 230000003179 granulation Effects 0.000 claims abstract description 7
- 238000002156 mixing Methods 0.000 claims description 3
- 238000001816 cooling Methods 0.000 claims description 2
- 239000003517 fume Substances 0.000 claims 1
- 239000004746 geotextile Substances 0.000 claims 1
- 239000004927 clay Substances 0.000 abstract description 6
- 230000018044 dehydration Effects 0.000 abstract description 5
- 238000006297 dehydration reaction Methods 0.000 abstract description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 4
- 238000003860 storage Methods 0.000 abstract description 3
- 238000000034 method Methods 0.000 description 7
- 239000010865 sewage Substances 0.000 description 7
- 238000001035 drying Methods 0.000 description 6
- 229910001385 heavy metal Inorganic materials 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 238000011049 filling Methods 0.000 description 2
- 239000008187 granular material Substances 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 239000004576 sand Substances 0.000 description 2
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 1
- 229910004298 SiO 2 Inorganic materials 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000004566 building material Substances 0.000 description 1
- 239000000969 carrier Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000001125 extrusion Methods 0.000 description 1
- 238000005187 foaming Methods 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 239000004615 ingredient Substances 0.000 description 1
- 231100001240 inorganic pollutant Toxicity 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 244000000010 microbial pathogen Species 0.000 description 1
- 244000052769 pathogen Species 0.000 description 1
- 239000008188 pellet Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
Images
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- 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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P40/00—Technologies relating to the processing of minerals
- Y02P40/60—Production of ceramic materials or ceramic elements, e.g. substitution of clay or shale by alternative raw materials, e.g. ashes
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- Treatment Of Sludge (AREA)
Abstract
Description
技术领域 technical field
本发明属于污泥处理技术领域,尤其涉及一种采用土工管袋脱水后的污泥烧制陶粒的系统。The invention belongs to the technical field of sludge treatment, and in particular relates to a system for firing ceramsite with sludge dehydrated by geotechnical tube bags.
背景技术 Background technique
随着我国经济的迅速发展和对环境保护的重视,城市生活污水和工业废水必须经过处理达到国家标准后才能排放,在此处理过程中污水中绝大部分污染物转移到污泥中,城市污泥是一类危害性极大的固体废弃物,含有病源微生物、有机无机污染物和重金属。目前我国城市污泥加上污染河湖疏浚污泥数量非常巨大并且持续增长,彻底的处理污泥,防止其二次污染是世界共同面临的问题,解决此问题刻不容缓。With the rapid development of my country's economy and the emphasis on environmental protection, urban domestic sewage and industrial wastewater must be treated to meet national standards before they can be discharged. During this process, most of the pollutants in the sewage are transferred to the sludge, and urban sewage Mud is a kind of extremely harmful solid waste, which contains pathogenic microorganisms, organic and inorganic pollutants and heavy metals. At present, the amount of urban sludge plus polluted river and lake dredging sludge in my country is very large and continues to grow. Thorough treatment of sludge and prevention of its secondary pollution are common problems faced by the world, and it is urgent to solve this problem.
通过对我国城市污泥及河道疏浚污泥主要化学成分的分析发现,其中含有的SiO2、Al2O3、Fe2O3、CaO、MgO的含量与粘土的成分相似,其配比满足烧制陶粒的要求,如果利用污泥烧制陶粒,不仅可以充分利用底泥中部分有机质作为陶粒焙烧过程中的发泡物质,而且底泥中的无机成分也得到了利用,高温焙烧可以完全将病原体杀灭,并把重金属固结在陶粒中,消除重金属的污染问题。Through the analysis of the main chemical components of urban sludge and river dredging sludge in China, it is found that the content of SiO 2 , Al 2 O 3 , Fe 2 O 3 , CaO, and MgO contained in it is similar to that of clay, and its proportion meets the requirements of burning. Requirements for making ceramsite. If sludge is used to burn ceramsite, not only can fully utilize part of the organic matter in the bottom mud as the foaming material in the ceramsite roasting process, but also the inorganic components in the bottom mud can be used. High temperature roasting can Completely kill pathogens, and consolidate heavy metals in ceramsite, eliminating the pollution of heavy metals.
陶粒是一种适应现代建筑轻型化、高性能化需要的新型混凝土骨料,它可以代替重量质砂石,成为轻质建筑材料生产和轻质混凝土的配料,可以大大减低成本,另外,污泥陶粒具有表面粗糙、比面积大和孔隙率高等特点,用作水处理滤料陶粒具有较强的优势和发展潜力。Ceramsite is a new type of concrete aggregate that meets the needs of modern buildings with light weight and high performance. It can replace heavy sand and gravel and become an ingredient in the production of lightweight building materials and lightweight concrete, which can greatly reduce costs. In addition, pollution Clay ceramsite has the characteristics of rough surface, large specific area and high porosity. It has strong advantages and development potential when used as water treatment filter material ceramsite.
发明内容 Contents of the invention
本发明提供一种重金属污染湖库底泥烧制陶粒的系统,此系统包括:The invention provides a system for firing ceramsite from the bottom mud of a heavy metal polluted lake reservoir, the system includes:
(1)污泥脱水单元(1) Sludge dehydration unit
采用土工管袋对城市污泥或河道湖库疏浚底泥进行脱水,在将污泥充填入土工管袋前加入絮凝剂,土工管袋充填满后固化干燥10到60天,待污泥含水率为45%~55%时,破袋将污泥取出。也可采用其它方式脱水如自然干化等到含水率为45%~55%Use geotechnical tube bags to dehydrate urban sludge or dredged sediment from rivers, lakes and reservoirs. Add flocculant before filling the sludge into geotechnical tube bags. After filling the geotechnical tube bags, they will be solidified and dried for 10 to 60 days. When it is 45% to 55%, break the bag to take out the sludge. It can also be dehydrated by other methods such as natural drying until the moisture content is 45% to 55%.
(2)混合造粒单元(2) Mixing and granulation unit
将含水率在50%左右的污泥与粘土类原料按体积比1∶1的比例在混料机中混匀,此比例下有利于形成容重低、比表面积高的优质陶粒,造粒采用挤压造粒工艺,成坯水分来自于半干底泥,不需要另外加水。Mix the sludge and clay raw materials with a moisture content of about 50% in the mixer at a ratio of 1:1 by volume. This ratio is conducive to the formation of high-quality ceramsite with low bulk density and high specific surface area. Extrusion granulation process, the moisture of the billet comes from the semi-dry bottom mud, no need to add water.
(3)污泥陶粒回转窑(3) Sludge ceramsite rotary kiln
成型后的污泥颗粒经皮带输送机送入陶粒回转窑,陶粒在回转窑中完成干燥、预热和焙烧过程,控制回转窑斜率在3.2%~4.5%,窑筒转速为2~3转/钟,窑内温度分布为干燥带180℃~320℃,预热带320℃~850℃,焙烧带1150℃~1200℃,冷却带800℃~350℃,陶粒出窑后冷却至室温,运输到陶粒储仓储藏。The formed sludge particles are sent to the ceramsite rotary kiln through the belt conveyor, and the ceramsite completes the drying, preheating and roasting process in the rotary kiln. Rotation per minute, the temperature distribution in the kiln is 180°C to 320°C in the drying zone, 320°C to 850°C in the preheating zone, 1150°C to 1200°C in the roasting zone, and 800°C to 350°C in the cooling zone. , transported to the ceramsite warehouse for storage.
本发明所用的原料主要是污水厂产生的污泥或湖库、河道疏浚的底泥,采用土工管袋脱水的方式使污泥含水率降低到45%~55%,污泥脱水过程耗能极小,破袋后取出污泥直接与粘土混合均匀后挤压造粒,造粒简单易操作,形成的陶粒坯体强度高。污水厂和河湖疏浚污泥具有较高的热值,污泥生料球焙烧时的热量一部分来自于污泥本身有机物的燃烧,减少耗能。经过干燥和预热处理后的污泥颗粒不会发生炸裂,并且烧制的陶粒结构均匀,具有高强度和大的比表面积,适用于污水处理中用于生物载体的生物陶粒要求或代替砂石添加在混凝土中。The raw materials used in the present invention are mainly sludge produced by sewage plants or bottom sludge dredged from lakes and rivers, and the water content of sludge is reduced to 45% to 55% by using geotechnical tube bag dehydration, and the sludge dehydration process consumes a lot of energy. Small size, after the bag is broken, take out the sludge and mix it with clay evenly, then extrude and granulate. The granulation is simple and easy to operate, and the formed ceramsite body has high strength. Dredging sludge from sewage plants and rivers and lakes has a high calorific value, and part of the heat when roasting sludge raw pellets comes from the combustion of organic matter in the sludge itself, reducing energy consumption. After drying and preheating, the sludge particles will not burst, and the fired ceramsite has a uniform structure, high strength and large specific surface area, which is suitable for biological ceramsite requirements or replacements for biological carriers in sewage treatment Sand and gravel are added to the concrete.
附图说明 Description of drawings
图1为烧制污泥陶粒系统图。Figure 1 is a system diagram of fired sludge ceramsite.
具体实施方式 Detailed ways
实施例1Example 1
将中新生态城汉沽污水库库底疏浚污泥在土工管袋中脱水,在土工管袋固化干燥15天后,含水率降到52%,脱水污泥与粘土按照质量比1∶1的比例在混料机中混合均匀,通过挤压机挤压成椭圆球形,然后进回转窑烧制,回转窑窑身斜率为3.5%,窑筒转速为2.5转/分,陶粒烧制周期为40~50分钟,出窑陶粒由斗式运输车运至陶粒储仓。The dredged sludge at the bottom of Hangu Sewage Reservoir in Sino-Singapore Eco-city was dehydrated in a geotechnical tube bag. After the geotechnical tube bag was solidified and dried for 15 days, the moisture content dropped to 52%. Mix evenly in the mixer, extrude into an ellipse through an extruder, and then enter the rotary kiln for firing. After 50 minutes, the ceramsite from the kiln is transported to the ceramsite storage warehouse by the bucket transport vehicle.
实施例2Example 2
采用污泥机械脱水装置将城市生活污泥含水率降到70~82%,再经过干化装置或自然干化将含水率降到50%,混料机混合质量比1∶1的脱水污泥和粘土,然后挤压成颗粒,通过皮带传送机送入回转窑喂料口,回转窑身斜率为4%,窑筒转速为2.5转/分,陶粒烧制周期为35~40分钟。Use a sludge mechanical dehydration device to reduce the moisture content of municipal domestic sludge to 70-82%, and then reduce the moisture content to 50% through a drying device or natural drying, and mix the dewatered sludge with a mass ratio of 1:1. and clay, and then extruded into granules, which are sent to the feed port of the rotary kiln through a belt conveyor. The slope of the rotary kiln body is 4%, the kiln drum speed is 2.5 rpm, and the ceramsite firing cycle is 35 to 40 minutes.
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CN2011203870484U CN202322657U (en) | 2011-10-13 | 2011-10-13 | System for firing ceramsite by using sludge |
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Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104402520A (en) * | 2014-11-25 | 2015-03-11 | 天津市彤均建材有限公司 | Method for producing preblended light aggregate concrete heat-preservation material |
CN104744017A (en) * | 2015-03-26 | 2015-07-01 | 四川省强途科技股份有限公司 | Sludge ceramsite preparation system |
CN109734418A (en) * | 2019-03-05 | 2019-05-10 | 中国华电科工集团有限公司 | The method and system of haydite are made by mixing with sludge for a kind of flyash |
-
2011
- 2011-10-13 CN CN2011203870484U patent/CN202322657U/en not_active Expired - Lifetime
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104402520A (en) * | 2014-11-25 | 2015-03-11 | 天津市彤均建材有限公司 | Method for producing preblended light aggregate concrete heat-preservation material |
CN104744017A (en) * | 2015-03-26 | 2015-07-01 | 四川省强途科技股份有限公司 | Sludge ceramsite preparation system |
CN109734418A (en) * | 2019-03-05 | 2019-05-10 | 中国华电科工集团有限公司 | The method and system of haydite are made by mixing with sludge for a kind of flyash |
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Address after: 300467, Tianjin, Tianjin new eco city road, creative building, building 5, seven floor Patentee after: Tianjin Ecology City Environmental Protection Co., Ltd. Patentee after: TIANJIN XINSHENG ENVIRONMENT DEVELOPMENT CO., LTD. Address before: 300467, Tianjin, Tianjin new eco city road, creative building, building 5, seven floor Patentee before: Tianjin Ecology City Environmental Protection Co., Ltd. Patentee before: Tianjin Ecology City Water Co.,Ltd. |
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Granted publication date: 20120711 |