CN103723999A - Method for preparing flower ceramic particles with urban water supply sludge - Google Patents

Method for preparing flower ceramic particles with urban water supply sludge Download PDF

Info

Publication number
CN103723999A
CN103723999A CN201310662703.6A CN201310662703A CN103723999A CN 103723999 A CN103723999 A CN 103723999A CN 201310662703 A CN201310662703 A CN 201310662703A CN 103723999 A CN103723999 A CN 103723999A
Authority
CN
China
Prior art keywords
ceramic particles
percent
rise rate
temperature rise
water supply
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
Application number
CN201310662703.6A
Other languages
Chinese (zh)
Other versions
CN103723999B (en
Inventor
李依丽
杨珊珊
李艳玲
尹晶
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Beijing University of Technology
Original Assignee
Beijing University of Technology
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Beijing University of Technology filed Critical Beijing University of Technology
Priority to CN201310662703.6A priority Critical patent/CN103723999B/en
Publication of CN103723999A publication Critical patent/CN103723999A/en
Application granted granted Critical
Publication of CN103723999B publication Critical patent/CN103723999B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/60Production of ceramic materials or ceramic elements, e.g. substitution of clay or shale by alternative raw materials, e.g. ashes

Landscapes

  • Cultivation Of Plants (AREA)
  • Fertilizers (AREA)
  • Treatment Of Sludge (AREA)

Abstract

A method for preparing flower ceramic particles with urban water supply sludge belongs to the field of environmental technology, and relates to the resource utilization of solid waste. Materials accounted by dry weight rate, including 30-50 percent of water supply sludge, 10-30 percent of coal slurry, 20-30 percent of flint clay, 5-7 percent of Chinese chestnut shell, 8-10 percent of waste glass and the like, are dried, grinded, mixed and uniformly agitated to be prepared into spheres 6-15 mm in particle diameter. The spheres are subjected to pre-heating torrefaction and cooling so as to form the high performance flower ceramic particles. The ceramic particles prepared by the method are light and have loose and porous surfaces, can absorb a considerable amount of water, and has proper ability to keep nutritious substances. Compared with soilless substrates such as sand and wood chips, the flow ceramic particles have the characteristics of cleanness, neatness, attractiveness in shape, lightness, no pollution, cleanable performance, durability, higher stability in chemical property and the like.

Description

Utilize city water mud to prepare the method for flower ceramsite
Technical field
The present invention is a kind of method of utilizing city water firing sludge high-performance flower ceramsite, belongs to environmental technology field.
Background technology
City water factory, when producing tap water, has also produced a large amount of mud.This part mud derives from filtering thing and the throw out producing in purificating raw water process, account for total water purification amount 4% ?7%, comprising suspended substance and the organism after concentrated, and remain in the coagulating agent in mud.Compare with sewage sludge, give coliform count in sewage sludge seldom, heavy metal content is also lower, has reduced the environmental threat that exceeds standard and bring due to bacterium and heavy metal contaminants.Seriously in short supply in current water resources, in the day by day serious situation of water environment pollution, for China, there is the more than 95% undressed present situation of sludge water condition in waterworks when precontract, the significance of sludge disposal is more and more subject to people's attention.
To for Chinese garden planting, be a kind of promising disposal options to sewage sludge at present, but due to higher to aluminium content in sewage sludge, can affect absorption and the metabolism of plant nutrient ingredient, so should use, still there is certain limitation.Water supply plant dewatered sludge is mainly by Fe 2o 3, Al 2o 3, SiO 2, the clay mineral such as CaO, MgO becomes to be grouped into, its character is similar to clay, has plasticity-, coking property, thermotolerance and adsorptivity.Be SiO 2content is on the low side, and plasticity-is not high enough, if replace clay to fire goods, can consider to add a certain amount of binding agent to improve plasticity-.Traditional flower ceramsite mainly be take leca as main, with replace clay to make haydite to sewage sludge, can not only change by the disease of spraining of making grain with local methods, dispose a large amount of mud it is innoxious simultaneously, and realized recycling, catered to the direction of China's light-weight aggregate Sustainable development.
Summary of the invention
The present invention utilizes and to sewage sludge, replaces the non-renewable Mineral resources such as clay to fire flower ceramsite.Specifically comprise the following steps:
(1) get respectively and cross 90~110 mesh sieves after flint clay, chestnut shell and waste glass crushing.
(2) get coal slime and be dried at 105 ℃, after water ratio 5%~10%, ground 100 mesh sieves.
(3) to giving in sewage sludge, add amendment, after fully stirring evenly, dewater, after dehydration, water ratio is about 75%;
(4) by the above-mentioned sewage sludge of giving, coal slime, flint clay, chestnut shell and cullet are by dry weight quality percentage composition 30%~50%, 10%~30%, 20%~30%, 5%~7%, 5%~10% mixing and stirring, and natural drying is made particle diameter after 2 days be the spherical of 6~15mm;
(5) after raw material ball is at room temperature dried to 1 day, send into and in retort furnace, carry out persistently overheating roasting, whole temperature-rise period is divided into 4 stages, the temperature rise rate of first stage is 15~30 ℃/min, the temperature rise rate of subordinate phase is 3~7 ℃/min, and phase III temperature rise rate is 5~15 ℃/min, and the last stage temperature rise rate is 35~45 ℃/min, wherein front three phases respectively lasts 20min, and a rear stage is lasted 10min.In second and third stage, should adopt slow intensification, be mainly for make organism be fully oxidized with pellet body in gas get rid of completely, to prevent that in its body, air scavenge makes base substrate occur defect not in time.
(6) by taking out after the raw material ball uniform decrease in temperature to 400 after roasting ℃, obtain high performance flower ceramsite.
The amendment of step (2) is the amendment of this area routine, and as high-efficiency polymerization aluminum chloride, its consumption is dewatered sludge amount 10%.
The advantage that the present invention has is: as the raw material of manufacturing haydite, make sewage sludge harmlessness when the high-temperature roasting to sewage sludge.Heavy metal is melted material through high-temperature roasting and is wrapped in haydite inside, and because of the organic substance that contains certain thermal value again, can provide heat for high-temperature roasting in mud, reduced certain energy consumption simultaneously, both reach the recycling of offal treatment, met again the requirement that industrialization is produced.
The features such as the flower ceramsite that the present invention produces has surface irregularity, loose porous, and specific surface area is large, stable chemical nature.Haydite can be good as soilless culture substrate water conservation draining ventilation property (can embody in an embodiment), and fertilizer-preserving ability is moderate, safety and sanitation, free from extraneous odour own, seldom grow worm's ovum and pathogen, also do not discharge objectionable impurities, be applicable to the soilless culture of the decorative flowers such as family, restaurant.
Concrete implementation method
Below by specific embodiment, the present invention is done to concrete introduction, following instance does not form limitation of the invention.
Embodiment 1:
Formula and the method for utilizing feedwater firing sludge flower ceramsite, concrete grammar is as follows:
(1) the high-efficiency polymerization aluminum chloride that adds dewatered sludge amount 10% to sewage sludge dewater to water ratio be 75%; other drying and grinding of respectively preparing burden are crossed after 100 mesh sieves according to stirring than the ratio of 30%:30%:30%:5%:5% to sewage sludge, coal slime, flint clay, chestnut shell and cullet dry weight; air-dry 2 days at normal temperatures, send into the spheroidal particle that tablets press is made 10mm.
(2) after raw material ball is at room temperature dried to 1 day, send into and in retort furnace, carry out persistently overheating roasting to 1000 ℃, whole temperature-rise period is divided into 4 stages, the temperature rise rate of first stage is 20 ℃/min, the temperature rise rate of subordinate phase is 5 ℃/min, and phase III temperature rise rate is 10 ℃/min, and the last stage temperature rise rate is 40 ℃/min, wherein front three phases respectively lasts 20min, and a rear stage is lasted 10min.
(3) by taking out after the raw material ball uniform decrease in temperature to 400 after roasting ℃, obtain high performance flower ceramsite.
The outward appearance of haydite finished product is the shaggy ball-type solid of Vandyke brown, tap density be 750 ?880kg/m 3, cylindrical compress strength 7.0MPa, water-intake rate is 13.6~20.8%.
Embodiment 2
The embodiment of the present embodiment is as different from Example 1: by step 2 Raw proportioning by sewage sludge, coal slime, flint clay, chestnut shell and cullet mix and mix thoroughly than the ratio of 40%:20%:25%:5%:10% in dry weight, and other steps and parameter are identical with embodiment 1.
The outward appearance of haydite finished product is the shaggy ball-type solid of Vandyke brown, tap density be 600 ?650kg/m 3, cylindrical compress strength 6.0MPa, water-intake rate is 14.7~19.4%.
Embodiment 3
The embodiment of the present embodiment is as different from Example 1: step 2 Raw proportioning is by sewage sludge, and coal slime, flint clay, chestnut shell and cullet mix and mix thoroughly than 50%:20%:20%:5%:5% by dry weight, and other steps and parameter are identical with embodiment 1.
The outward appearance of haydite finished product is the shaggy ball-type solid of chocolate, tap density be 520 ?580kg/m 3, cylindrical compress strength is 4.5MPa, water-intake rate is 17.5~26.2%.

Claims (2)

1. utilize the method for preparing flower ceramsite to sewage sludge, it is characterized in that, comprise the following steps:
(1) get respectively and cross 90~110 mesh sieves after flint clay, chestnut shell and waste glass crushing;
(2) get coal slime and be dried at 105 ℃, after water ratio 5%~10%, ground 100 mesh sieves;
(3) to giving in sewage sludge, add amendment, after fully stirring evenly, dewater, after dehydration, water ratio is about 75%;
(4) by the above-mentioned sewage sludge of giving, coal slime, flint clay, chestnut shell and cullet are by dry weight quality percentage composition 30%~50%, 10%~30%, 20%~30%, 5%~7%, 5%~10% mixing and stirring, and natural drying is made particle diameter after 2 days be the spherical of 6~15mm;
(5) after raw material ball is at room temperature dried to 1 day, send into and in retort furnace, carry out persistently overheating roasting, whole temperature-rise period is divided into 4 stages, the temperature rise rate of first stage is 15~30 ℃/min, the temperature rise rate of subordinate phase is 3~7 ℃/min, and phase III temperature rise rate is 5~15 ℃/min, and the last stage temperature rise rate is 35~45 ℃/min, wherein front three phases respectively lasts 20min, and a rear stage is lasted 10min;
(6) by taking out after the raw material ball uniform decrease in temperature to 400 after roasting ℃, obtain high performance flower ceramsite.
2. according to the method for claim 1, it is characterized in that, amendment is high-efficiency polymerization aluminum chloride, and its consumption is dewatered sludge amount 10%.
CN201310662703.6A 2013-12-09 2013-12-09 City water mud is utilized to prepare the method for flower ceramsite Expired - Fee Related CN103723999B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310662703.6A CN103723999B (en) 2013-12-09 2013-12-09 City water mud is utilized to prepare the method for flower ceramsite

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310662703.6A CN103723999B (en) 2013-12-09 2013-12-09 City water mud is utilized to prepare the method for flower ceramsite

Publications (2)

Publication Number Publication Date
CN103723999A true CN103723999A (en) 2014-04-16
CN103723999B CN103723999B (en) 2016-01-20

Family

ID=50448337

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310662703.6A Expired - Fee Related CN103723999B (en) 2013-12-09 2013-12-09 City water mud is utilized to prepare the method for flower ceramsite

Country Status (1)

Country Link
CN (1) CN103723999B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107337568A (en) * 2017-08-25 2017-11-10 洛阳茂生生物技术有限公司 A kind of method that the sludge substrate suitable for flower plants and nursery stock is prepared based on plant refuse
CN110885241A (en) * 2018-09-07 2020-03-17 何钢 Mullite-structure ceramic porous water storage material and preparation method thereof

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101148346A (en) * 2007-09-04 2008-03-26 山东大学 Method for preparing haydite from urban sewage plant sludge
CN101215150A (en) * 2008-01-18 2008-07-09 北京工业大学 Method for burning haydite by solid castoff

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101148346A (en) * 2007-09-04 2008-03-26 山东大学 Method for preparing haydite from urban sewage plant sludge
CN101215150A (en) * 2008-01-18 2008-07-09 北京工业大学 Method for burning haydite by solid castoff

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107337568A (en) * 2017-08-25 2017-11-10 洛阳茂生生物技术有限公司 A kind of method that the sludge substrate suitable for flower plants and nursery stock is prepared based on plant refuse
CN110885241A (en) * 2018-09-07 2020-03-17 何钢 Mullite-structure ceramic porous water storage material and preparation method thereof

Also Published As

Publication number Publication date
CN103723999B (en) 2016-01-20

Similar Documents

Publication Publication Date Title
CN104163617B (en) The application of a kind of haydite production method and haydite and haydite
CN103693943B (en) Method for firing ceramsite with sludge dehydrated through conditioning
CN104261802B (en) A kind of mud flyash high-strength ceramic granule and preparation method thereof
CN102815965B (en) Porous ceramsite made of low-silicon iron tailings and preparation method of porous ceramsite
CN101585672B (en) Biosolid-sludge mixed ceram site
CN110078530B (en) Preparation method of high-performance sintered insulating brick
CN103145442A (en) Method for preparing non-sintered ceramisites by using chemical sludge
CN109251012A (en) A method of light ceramic is prepared using sludge and copper ashes
CN108585934A (en) A kind of aluminium sludge ceramsite preparation method
CN105036709B (en) A kind of utilization sewage sludge, flyash burn the preparation method of lightweight tourmaline haydite
CN103011769A (en) Method for producing light-weight energy-saving brick for buildings from municipal sludge
CN107188601A (en) A kind of method that utilization city sewage and sludge prepares light porous haydite
CN103030371A (en) Method for manufacturing brick by high-content municipal sludge
CN103011768A (en) Method for firing paving brick by recycling municipal sludge
CN101560110B (en) Spherical light porous material for wastewater treatment
CN102173745A (en) Method for baking ceramsite by using town sludge, loess and iron ore powder
CN102173747A (en) Method for firing haydite from municipal sludge, loess and bentonite
CN106116508A (en) A kind of method utilizing municipal sludge to produce anti-blocking sintering brick permeable to water for pore creating material
CN103030364A (en) Method for manufacturing floor tile by municipal sludge
CN109384405A (en) A kind of high-strength ceramic granule and the method and system that it is prepared using municipal sludge
CN104761111A (en) Preparation method of rice husk powder conditioning sludge incineration slag and method for conditioning urban sludge
CN107129270A (en) A kind of method for mixing cinder and firing ceramsite by using sludge
CN107216124A (en) One kind utilizes sewage sludge sintering heat insulation building block and its method
CN110723961A (en) Environment-friendly microporous brick prepared by comprehensively utilizing solid wastes and preparation method thereof
CN103723999B (en) City water mud is utilized to prepare the method for flower ceramsite

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
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20160120

Termination date: 20191209