CN102515835A - Construction residual soil sludge sintered brick doped with household garbage particles and its preparation method - Google Patents
Construction residual soil sludge sintered brick doped with household garbage particles and its preparation method Download PDFInfo
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- CN102515835A CN102515835A CN201110405821XA CN201110405821A CN102515835A CN 102515835 A CN102515835 A CN 102515835A CN 201110405821X A CN201110405821X A CN 201110405821XA CN 201110405821 A CN201110405821 A CN 201110405821A CN 102515835 A CN102515835 A CN 102515835A
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- household garbage
- fuel
- garbage particles
- architecture sediment
- brick
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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
- 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
- Y02W30/58—Construction or demolition [C&D] waste
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- Processing Of Solid Wastes (AREA)
Abstract
The invention discloses a construction residual soil sludge sintered brick doped with household garbage particles and its preparation method. The sintered brick is composed of the following raw materials by mass: 45-80% of construction residual soil, 10-35% of urban sludge, and 15-30% of an interior fuel. Specifically, with a particle size less than 3mm and a water content of 10%, the interior fuel comprises the components with the following mass percents in the raw materials of the sintered brick: 5-15% of coal slag and coal gangues, and 8-15% of household garbage particles, which are selected from combustible particles that undergo crushing, sorting, and dehydration pretreatments. The method of the invention makes fully use of urban construction residual soil, urban sludge, household garbage and other wastes, and changes waste materials into things of value. And the prepared sintered brick has superior physical and mechanical performances, low production cost, and is energy saving and environment friendly.
Description
Technical field
The present invention is specifically related to a kind of architecture sediment sludge baked brick that is mixed with household garbage particles and preparation method thereof.
Background technology
China's building trade is huge to the demand of vitrified brick, prepares vitrified brick in the past and is to utilize to take the farmland clay and process through sintering, thereby cause soil resource to run off in a large number, and it is quite serious to ruin the field phenomenon.Country has forbidden using and producing of clay solid brick at present, adopts riverslakes sludge or architecture sediment brickmaking to become the trend of instead of clay brickmaking.
Chinese patent (CN200910184633.1) provides a kind of mud sludge baked brick; But peri-urban is not all to have a large amount of riverslakes sludges to utilize mostly; But continuous speed-raising along with urbanization process; Architecture sediment becomes the geometry level speed increment, and its resource utilization becomes the problem that presses for solution.Adopt architecture sediment to replace mud, preparation architecture sediment sludge baked brick becomes a kind of urban waste recycling scheme of more feasible more environmental protection.Also propose in the Chinese patent (CN200910184633.1) to prepare vitrified brick as fuel through burning the method for losing with wood chip, straw, cinder etc.; But the pore structure of this method preparation is not ideal enough; Be unfavorable for the reduction of thermal conductivity; And a large amount of collection the such as wood chip, straw had any problem, and the source is unstable relatively.(riverway sludge is produced the technical study of vitrified brick to father-in-law's Jingjing; Zhejiang University's master thesis) it is proposed to improve, adopt expanded polystyrene particle as fuel, to form good circular port structure; But the raw material relative cost is high; And granules of polystyrene burning is to discharge toxic gas, cause environmental pollution, and subsequent treatment cost is higher.
Summary of the invention
The objective of the invention is the defective that exists in the prior art in order to solve, it is that raw material, cost are low that a kind of urban waste that is easy to get that makes full use of is provided, and energy-conservation vitrified brick and preparation method thereof.
In order to achieve the above object, the invention provides a kind of architecture sediment sludge baked brick that is mixed with household garbage particles, form by the raw material of following mass percent:
Architecture sediment: 45~80%,
Municipal sludge: 10~35%,
Fuel: 15~30%;
Wherein, the particle diameter of fuel is less than 3mm, and water ratio is 10%, and the component of fuel and each component shared mass percent in the raw material of said vitrified brick are:
Cinder and coal gangue: 5~15%,
Household garbage particles: 8~15%;
Wherein, household garbage particles is selected from through pulverizing, sorting and dehydration pretreatment combustiblematerials particle.
The present invention also provides a kind of preparation method who is mixed with the architecture sediment sludge baked brick of household garbage particles, may further comprise the steps:
(1) architecture sediment and mud collection: the exploitation architecture sediment, subsequent use after storing ageing, municipal sludge is stacked evenly subsequent use;
(2) batching: the architecture sediment and the municipal sludge of said weight percent are mixed, stir moisturizing the time then, even until moisture, denseness is moderate;
(3) domestic refuse collection: household garbage particles is selected from through pulverizing, sorting and the pretreated combustiblematerials particle of dehydrating step;
(4) fuel screening: get said fuel by said mass percent, the screening of broken back, the preparation particle diameter is subsequent use less than the particle of 3mm;
(5) fuel is mixed and is joined: above-mentioned fuel particle is spiked in the mixture of above-mentioned architecture sediment and municipal sludge, utilizes stirrer to stir;
(6) extrusion molding: utilize mud extruder that above-mentioned mixed raw material is pushed, on brick cutting machine, cut base then and form adobe;
(7) drying: adobe piled up in the base field carry out natural drying, be aided with the kiln drying means then and carry out artificial seasoning;
(8) roasting, finished product: in annular kiln, carry out sintering to above-mentioned through dried adobe, the agglomerating temperature is 945~1000 ℃, and kiln discharge promptly makes this product then.
The present invention compares prior art and has the following advantages: the present invention has made full use of urban architecture dregs, municipal sludge the like waste, and the vitrified brick physical and mechanical property of processing is superior, and production cost is low, and energy-conserving and environment-protective.Adopt the flammable organism that sub-elects in the domestic refuse to substitute wood chip, stalk etc., raw material sources extensively, be easy to get, production cost is low.But the flammable organism spontaneous combustion in roasting process in the domestic refuse, conserve energy forms vesicular structure after the roasting simultaneously in vitrified brick, improved heat-insulating property, again domestic refuse has been carried out recycling, environmental protection and energy saving.
Embodiment
Architecture sediment sludge baked brick that the present invention is mixed with household garbage particles below in conjunction with embodiment and preparation method thereof is elaborated.
Product embodiments 1
Vitrified brick of the present invention is made up of the raw material of following mass percent: 45% architecture sediment, 30% municipal sludge, 15% cinder and coal gangue and 10% household garbage particles.Household garbage particles is selected from the flammable organism that sub-elects, this flammable organism and cinder and coal gangue after crushed, particle diameter is 2.8mm, water ratio 10%.
Product embodiments 2
Vitrified brick of the present invention is made up of the raw material of following mass percent: 55% architecture sediment, 20% municipal sludge, 10% cinder and coal gangue and 15% household garbage particles.Household garbage particles is selected from the flammable organism that sub-elects, this flammable organism and cinder and coal gangue after crushed, particle diameter is 2.5mm, water ratio 10%.
Product embodiments 3
Vitrified brick of the present invention is made up of the raw material of following mass percent: 70% architecture sediment, 10% municipal sludge, 10% cinder and coal gangue and 10% household garbage particles.Household garbage particles is selected from the flammable organism that sub-elects, this flammable organism and cinder and coal gangue after crushed, particle diameter is 2.5mm, water ratio 10%.
Preparation embodiment
Utilize above-mentioned 3 described proportioning raw materials of product embodiments, be mixed with the preparation of the architecture sediment sludge baked brick of household garbage particles respectively, concrete preparation method is following:
(1) architecture sediment and mud collection: carry out the architecture sediment exploitation, subsequent use after ageing, municipal sludge is stacked evenly subsequent use;
(2) batching: the architecture sediment and the municipal sludge of said weight percent are mixed, stir moisturizing the time then, even until moisture, denseness is moderate;
(3) domestic refuse collection: household garbage particles is selected from through step pre-treatment such as pulverizing, sorting and dehydration, the combustiblematerials particle that obtains;
(4) fuel screening: get said fuel by said mass percent, the screening of broken back, the preparation particle diameter is subsequent use less than the particle of 3mm;
(5) fuel is mixed and is joined: above-mentioned fuel particle is spiked in the mixture of above-mentioned architecture sediment and municipal sludge, utilizes stirrer to stir;
(6) extrusion molding: utilize mud extruder that above-mentioned mixed raw material is pushed, on brick cutting machine, cut base then and form adobe;
(7) drying: adobe piled up in the base field carry out natural drying, be aided with the kiln drying means then and carry out artificial seasoning;
(8) roasting, finished product: in annular kiln, carry out sintering to above-mentioned through dried adobe, the agglomerating temperature is 945~1000 ℃, and kiln discharge promptly makes this product then.
Effect embodiment
According to the prescription and the preparation method of the described vitrified brick of the foregoing description, the physical and mechanical property of the vitrified brick that obtains is following:
Table 1 is mixed with the architecture sediment sludge baked brick physical and mechanical property of household garbage particles
Stem body amasss density (kg/m 3) | Ultimate compression strength (MPa) | Equivalent heat conductivity (W/ (mK)) | Heat storage coefficient (W/ (m 2·K)) |
1300~1450 | 8.5~11.5 | 0.30~0.35 | 5.8~6.9 |
By knowing that it is superior that the present invention is mixed with the architecture sediment sludge baked brick physical and mechanical property of household garbage particles in the table, domestic refuse, architecture sediment and municipal sludge have obtained fully effectively utilizing energy-conserving and environment-protective simultaneously.
Claims (2)
1. architecture sediment sludge baked brick that is mixed with household garbage particles, it is characterized in that: said vitrified brick is made up of the raw material of following mass percent:
Architecture sediment: 45~80%,
Municipal sludge: 10~35%,
Fuel: 15~30%;
The particle diameter of said fuel is less than 3mm, and water ratio is 10%, and the component of fuel and each component shared mass percent in the raw material of said vitrified brick are:
Cinder and coal gangue: 5~15%,
Household garbage particles: 8~15%;
Said household garbage particles is selected from through pulverizing, sorting and the pretreated combustiblematerials particle of dehydration.
2. preparation method who is mixed with the architecture sediment sludge baked brick of household garbage particles according to claim 1 is characterized in that: may further comprise the steps:
(1) architecture sediment and mud collection: the exploitation architecture sediment, subsequent use after storage, ageing, municipal sludge is stacked evenly subsequent use;
(2) batching: the architecture sediment and the municipal sludge of said weight percent are mixed, stir moisturizing the time then, even until moisture, denseness is moderate;
(3) domestic refuse collection: domestic refuse through step pre-treatment such as pulverizing, magnetic separation and dehydrations, can be used for burning electricity generation, and household garbage particles is subsequent use after the collection pre-treatment;
(4) fuel screening: get said fuel by said mass percent, the screening of broken back, the preparation particle diameter is subsequent use less than the particle of 3mm;
(5) fuel is mixed and is joined: above-mentioned fuel particle is spiked in the mixture of above-mentioned architecture sediment and municipal sludge, utilizes stirrer to stir;
(6) extrusion molding: utilize mud extruder that above-mentioned mixed raw material is pushed, on brick cutting machine, cut base then and form adobe;
(7) drying: adobe piled up in the base field carry out natural drying, be aided with the kiln drying means then and carry out artificial seasoning;
(8) roasting, finished product: in annular kiln, carry out sintering to above-mentioned through dried adobe, the agglomerating temperature is 945~1000 ℃, and kiln discharge promptly makes this product then.
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Cited By (17)
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CN102765927A (en) * | 2012-07-05 | 2012-11-07 | 浙江特拉建材有限公司 | Brick making method |
CN102795877A (en) * | 2012-08-29 | 2012-11-28 | 浙江嘉荣新型材料有限公司 | Energy-saving heat retaining rectangular-hole porous brick |
CN105272159A (en) * | 2015-11-01 | 2016-01-27 | 十堰红玉新型墙材有限公司 | Production method of sludge sintered brick |
CN106116482A (en) * | 2016-06-22 | 2016-11-16 | 福建工程学院 | The method utilizing mineralized waste, mud and building castoff sintering self-insulating brick |
CN106111661A (en) * | 2016-06-24 | 2016-11-16 | 福鼎市利民城市建筑垃圾处理有限公司 | A kind of refuse classification processing method |
CN106699125A (en) * | 2017-03-02 | 2017-05-24 | 陈炳响 | Sintered brick and preparation method thereof |
CN107056238A (en) * | 2017-04-10 | 2017-08-18 | 河南永泽环境科技有限公司 | A kind of method of anaerobic sludge digestion biogas residue brickmaking |
CN107098680A (en) * | 2016-02-23 | 2017-08-29 | 汪风珍 | Producing bricks from refuse |
CN107352965A (en) * | 2017-08-01 | 2017-11-17 | 合肥广民建材有限公司 | A kind of novel clinker brick and preparation method |
CN108947483A (en) * | 2018-09-06 | 2018-12-07 | 西安墙体材料研究设计院有限公司 | A kind of method that sludge compound mineralization rubbish prepares wall body brick material |
CN109694235A (en) * | 2018-11-22 | 2019-04-30 | 王�锋 | A kind of method and apparatus that rubbish consumption recycles |
CN110257124A (en) * | 2018-12-29 | 2019-09-20 | 王�锋 | The method of rubbish biomass burning block and preparation method thereof and systems of distributed heating systems and power generation |
CN110668788A (en) * | 2019-10-17 | 2020-01-10 | 湖北玉鑫新型墙材有限公司 | Method for making bricks by using sludge wastewater |
CN111908942A (en) * | 2020-08-11 | 2020-11-10 | 南京鑫翔新型建筑材料有限责任公司 | Method for preparing modulus perforated brick from sludge and urban muck |
CN113979724A (en) * | 2021-10-28 | 2022-01-28 | 青岛农业大学 | Sintered brick and preparation method and application thereof |
CN114436673A (en) * | 2022-03-11 | 2022-05-06 | 筑邦建筑科技投资(深圳)有限公司 | Ultra-long light silica spar wallboard and preparation method |
CN115144032A (en) * | 2022-07-01 | 2022-10-04 | 东北林业大学 | Complex environment simulation test system and test method suitable for forest combustible |
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CN1325769A (en) * | 2001-06-27 | 2001-12-12 | 陈恩清 | Technology for making sintered garbage brick |
CN101672085A (en) * | 2009-08-26 | 2010-03-17 | 江苏康斯维信建筑节能技术有限公司 | Baked brick of riverslakes sludge and municipal sludge and production method thereof |
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CN1072915A (en) * | 1991-12-02 | 1993-06-09 | 张守仁 | Method with making brick with daily garbage |
CN1109850A (en) * | 1995-01-25 | 1995-10-11 | 北京市环境卫生科学研究所 | Method for producing haydite from refuse or mud |
CN1325769A (en) * | 2001-06-27 | 2001-12-12 | 陈恩清 | Technology for making sintered garbage brick |
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Cited By (21)
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CN102765927A (en) * | 2012-07-05 | 2012-11-07 | 浙江特拉建材有限公司 | Brick making method |
CN102795877A (en) * | 2012-08-29 | 2012-11-28 | 浙江嘉荣新型材料有限公司 | Energy-saving heat retaining rectangular-hole porous brick |
CN105272159A (en) * | 2015-11-01 | 2016-01-27 | 十堰红玉新型墙材有限公司 | Production method of sludge sintered brick |
CN105272159B (en) * | 2015-11-01 | 2018-11-06 | 十堰红玉新型墙材有限公司 | A kind of production method of sludge baked brick |
CN107098680A (en) * | 2016-02-23 | 2017-08-29 | 汪风珍 | Producing bricks from refuse |
CN106116482A (en) * | 2016-06-22 | 2016-11-16 | 福建工程学院 | The method utilizing mineralized waste, mud and building castoff sintering self-insulating brick |
CN106111661A (en) * | 2016-06-24 | 2016-11-16 | 福鼎市利民城市建筑垃圾处理有限公司 | A kind of refuse classification processing method |
CN106699125A (en) * | 2017-03-02 | 2017-05-24 | 陈炳响 | Sintered brick and preparation method thereof |
CN107056238A (en) * | 2017-04-10 | 2017-08-18 | 河南永泽环境科技有限公司 | A kind of method of anaerobic sludge digestion biogas residue brickmaking |
CN107352965A (en) * | 2017-08-01 | 2017-11-17 | 合肥广民建材有限公司 | A kind of novel clinker brick and preparation method |
CN108947483A (en) * | 2018-09-06 | 2018-12-07 | 西安墙体材料研究设计院有限公司 | A kind of method that sludge compound mineralization rubbish prepares wall body brick material |
WO2020048402A1 (en) * | 2018-09-06 | 2020-03-12 | 西安墙体材料研究设计院有限公司 | Method for preparation of wall bricks from sludge composite mineralized waste |
CN108947483B (en) * | 2018-09-06 | 2020-10-02 | 西安墙体材料研究设计院有限公司 | Method for preparing wall brick from sludge composite mineralized garbage |
CN109694235A (en) * | 2018-11-22 | 2019-04-30 | 王�锋 | A kind of method and apparatus that rubbish consumption recycles |
CN109694235B (en) * | 2018-11-22 | 2022-05-03 | 王�锋 | Method and device for garbage absorption and reutilization |
CN110257124A (en) * | 2018-12-29 | 2019-09-20 | 王�锋 | The method of rubbish biomass burning block and preparation method thereof and systems of distributed heating systems and power generation |
CN110668788A (en) * | 2019-10-17 | 2020-01-10 | 湖北玉鑫新型墙材有限公司 | Method for making bricks by using sludge wastewater |
CN111908942A (en) * | 2020-08-11 | 2020-11-10 | 南京鑫翔新型建筑材料有限责任公司 | Method for preparing modulus perforated brick from sludge and urban muck |
CN113979724A (en) * | 2021-10-28 | 2022-01-28 | 青岛农业大学 | Sintered brick and preparation method and application thereof |
CN114436673A (en) * | 2022-03-11 | 2022-05-06 | 筑邦建筑科技投资(深圳)有限公司 | Ultra-long light silica spar wallboard and preparation method |
CN115144032A (en) * | 2022-07-01 | 2022-10-04 | 东北林业大学 | Complex environment simulation test system and test method suitable for forest combustible |
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Application publication date: 20120627 |