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CN106865926A - One kind has filled municipal sludge curing agent and its deep dehydration method - Google Patents

One kind has filled municipal sludge curing agent and its deep dehydration method Download PDF

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Publication number
CN106865926A
CN106865926A CN201710137689.6A CN201710137689A CN106865926A CN 106865926 A CN106865926 A CN 106865926A CN 201710137689 A CN201710137689 A CN 201710137689A CN 106865926 A CN106865926 A CN 106865926A
Authority
CN
China
Prior art keywords
sludge
curing agent
municipal sludge
deep dehydration
landfill
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.)
Pending
Application number
CN201710137689.6A
Other languages
Chinese (zh)
Inventor
张晴波
陈海斌
郑世华
张守献
张露
钟煌亮
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.)
CCCC National Engineering Research Center of Dredging Technology and Equipment Co Ltd
Original Assignee
CCCC National Engineering Research Center of Dredging Technology and Equipment Co Ltd
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 CCCC National Engineering Research Center of Dredging Technology and Equipment Co Ltd filed Critical CCCC National Engineering Research Center of Dredging Technology and Equipment Co Ltd
Priority to CN201710137689.6A priority Critical patent/CN106865926A/en
Publication of CN106865926A publication Critical patent/CN106865926A/en
Pending legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/008Sludge treatment by fixation or solidification
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/121Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
    • C02F11/122Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering using filter presses
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/14Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Mechanical Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Treatment Of Sludge (AREA)

Abstract

本发明公开了一种已填埋市政污泥固化剂及其深度脱水方法,属于市政污泥处理领域。填埋市政污泥一方面在填埋前已添加一定比例固化剂,增加了二次深度脱水处理难度,另一方面填埋污泥在厌氧环境中发生复杂的生化反应,含水率又会增加,且污泥成分变得更加复杂。针对填埋市政污泥特性,使用固化剂包括电石渣、硫铝酸盐水泥、矿粉、粉煤灰和铁盐,按一定的污泥干基百分比、添加顺序和搅拌时间添加,对污泥进行调理,有效改善污泥的脱水性能,使污泥中的胶体颗粒脱稳、絮凝,脱去大量水分,为污泥的深度脱水营造基础条件,脱水后泥饼含水率可降至50%‑60%。本发明解决了已填埋市政污泥深度脱水问题,脱水后污泥可作资源化利用。固化剂易于获得且价格低廉。The invention discloses a solidifying agent for landfilled municipal sludge and a deep dehydration method thereof, belonging to the field of municipal sludge treatment. On the one hand, a certain proportion of curing agent has been added to landfill municipal sludge, which increases the difficulty of secondary deep dehydration treatment. On the other hand, landfill sludge undergoes complex biochemical reactions in an anaerobic environment, and the moisture content will increase. , and the sludge composition becomes more complex. According to the characteristics of landfill municipal sludge, solidifying agents including calcium carbide slag, sulphoaluminate cement, mineral powder, fly ash and iron salt are used according to a certain percentage of sludge dry basis, adding order and stirring time. Conditioning can effectively improve the dehydration performance of the sludge, destabilize and flocculate the colloidal particles in the sludge, remove a large amount of water, and create basic conditions for the deep dehydration of the sludge. After dehydration, the moisture content of the mud cake can be reduced to 50%‑ 60%. The invention solves the problem of deep dehydration of landfilled municipal sludge, and the dehydrated sludge can be used for resource utilization. Curing agents are readily available and inexpensive.

Description

One kind has filled municipal sludge curing agent and its deep dehydration method
Technical field
Municipal sludge curing agent and its deep dehydration side have been filled the invention belongs to field of sludge treatment, more particularly to one kind Method.
Background technology
Substantial amounts of sludge can be produced in sewage disposal process, its quality accounts for processing the 0.3%-0.5% of water, by In the end of the year 2015, the sludge yield of national urban wastewater treatment firm is up to more than 35,000,000 tons/year, it is contemplated that to the year two thousand twenty, sludge yield Will be up to 60,000,000 tons/year.Current sludge treatment approach topmost in the world includes agricultural use, sanitary landfills, burning and sea Ocean jettisons, and China mainly uses the methods such as landfill, compost, desiccation, burning for the treatment and disposal of sludge, at these four Reason mode accounting is respectively 65%, 15%, 6% and 3%.Consider environmental benefit and economic benefit, whole nation cities and towns are dirty at present The sludge of water treatment plant has turned into the major way of China's sludge treatment by carrying out sanitary landfills after press filtration, and following one Still will be the main sludge treating method of China in individual period.
China's land resource is limited, and the sludge for continually producing is caused by landfill to surrounding enviroment and the ecosystem Many harm, and the land resource of preciousness is taken, especially in the eastern region that China's land resource is the most in short supply, without conjunction When suitable disposal technology and no extraneous region is available for Sludge landfill, will fill the further volume reduction of sludge turns into what is explored now Direction.
Sludge components are complicated, are the collection of organic matter and the inorganic matter composition of the zoogloea and its absorption of multiple-microorganism formation Zoarium, in sludge in addition to containing substantial amounts of moisture, also containing heavy metal, hardly degraded organic substance and salt, and pathogen, virus Microorganism and parasitic ovum etc., with easy smelly, perishable property.Because the high-hydrophilic of sludge to it, it is necessary to adjust Manage to change the physicochemical characteristics and component on mud granule surface, so that the colloform texture destroyed inside sludge, reaches improvement The purpose of dewatering performance of sludge.Press《Consumer waste filling and embedding Environmental capacity standard》(GB16889-2008) specify:At sanitary sewage Reason factory sludge moisture content after treatment is less than 60% can just enter household refuse landfill sites landfill stabilization.Therefore it is new to produce dirt Mud can be nursed one's health in sewage treatment plant by dosing, and carry out landfill after press filtration.So, landfill municipal sludge is on the one hand added Curing agent is crossed, the biochemistry that further deep dehydration difficulty is bigger, and on the other hand complexity can occur in sludge sump is filled is carried out Reaction, moisture content can increase again, and sludge components become more complicated.And at present for the research of curing agent and its dewatering And application is concentrated mainly on river and lake silt and fresh municipal sludge, for having filled municipal sludge curing agent and its deep dehydration The research of method there is no precedent.This is directed to, the present invention is proposed.
The content of the invention
The technical problems to be solved by the invention be to provide a kind of low cost, process time is short, sedimentation rate of impurities The fast, municipal sludge of the landfill curing agent and its deep dehydration method that degree of dehydration is high.
To realize above-mentioned technical problem, the technical scheme that the present invention is provided is:
One kind landfill municipal sludge curing agent, it is characterised in that:
The curing agent includes carbide slag, sulphate aluminium cement, miberal powder, flyash and molysite, each group in the curing agent Split-phase is respectively for the percentage of sludge butt:
Carbide slag:37.5%-62.5%;
Sulphate aluminium cement:12.5%-25%;
Miberal powder:6.25%-12.5%;
Flyash:6.25%-12.5%;
Molysite:2.75%-3.25%.
Above-mentioned sludge butt refers to the quality of over dry sludge in wet mud.
The dewatering of the above-mentioned curing agent that the present invention is used is:
(1) after carbide slag being dissolved in into water, add under agitation, stir 5-10min, make mixing more uniform.Calcium carbide Slag main component is calcium hydroxide, also there is the calcium carbide not reacted completely, can meet water and react, and releases substantial amounts of heat, and Generation calcium hydroxideIts effect and the basically identical (CaO+H of quick lime2O=Ca (OH)2), the free water in sludge can be sloughed;Calcium ion can be with electronegative group knot in sludge extracellular polymeric (EPS) Close, increase floc strength, isolate the combination water in sludge.
(2) sulphate aluminium cement is subsequently added into, 3-5min is stirred.Sulphate aluminium cement is mainly with anhydrous sulphur (iron) aluminic acid Calcium and dicalcium silicate are the novel concrete of main mineral composition.
(3) miberal powder is added after, 3-5min is stirred.After miberal powder generally refers to for mined ore to carry out pulverizing processing Resulting feed powder.
(4) flyash is added, 5-8min is stirred.Mainly by SiO2、CaO、Al2O3, MgO, FeO and Fe2O3Deng chemicals Matter is constituted, and particle inside easily forms loose structure, and specific surface area is larger, high adsorption capacity, after mixing with sludge, destroys sludge The stabilization of colloidal solid, mutual aggregation forms bulky grain between making scattered little particle, produces and electrically neutralize and adsorption bridging Effect, can isolate sludge absorption water.
(5) molysite is eventually adding, the sludge after conditioning is pumped into filter press after stirring 10-15min carries out press filtration.Using dirt The electronegativity of mud and the polar group on mud granule surface, add the Ferric Salt Flocculants of positively charged, by compressing colloid electric double layer With the reagentia such as absorption-charge neutrality, so as to improve the dewatering of sludge, make the de- steady, flocculation of colloidal solid.Described molysite It is ferric trichloride or ferric sulfate etc..
Present invention has the advantages that:
(1) effect of carbide slag in sludge dewatering conditioning is basically identical with quick lime, can effectively slough the trip in sludge From water and water is combined, its price is only the 1/4-1/5 of quick lime.
(2) sulphate aluminium cement can have special efficiency to poisonous, harmful components consolidations in sludge, and miberal powder can increase de- Mud cake intensity after water, therefore addition sulphate aluminium cement and miberal powder can further promote the resource profit after sludge conditioning dehydration With, greening soil can be made, compost is disposed, brickmaking, haydite etc..
(3) flyash has larger discharge capacity as a kind of common industrial residue in China, cheap, and itself is again Belong to easily dehydration material, the curing agent to be formed is combined with carbide slag can both improve dewatering performance of sludge, and generation is solidifying rigid to answer Miscellaneous hydroxide, occurs electrically to neutralize the volume effect of sweeping, and forms big more uniform flocculation structure, and sludge can be controlled again pH。
(4) molysite belongs to inorganic sludge conditioning flocculant, and flocculating effect is good, and price is cheap compared with aluminium salt, is wadded a quilt with cotton compared to macromolecule It is more simple and easy to get for solidifying agent.
(5) with above-mentioned landfill municipal sludge curing agent and its dewatering, can make it is added cross curing agent, in sludge There is the biochemical reaction of complexity in hole, moisture content increases, composition becomes more complicated landfill municipal sludge and slough a large amount of water Point, moisture content of the cake can be down to 50%-60% after dehydration, and mud cake intensity is big, and harmful components are few, be conducive to follow-up resource profit With.
Specific embodiment
Municipal sludge curing agent and its deep dehydration method have been filled the invention discloses one kind.The landfill side of municipal sludge one Certain proportion curing agent and high polymer coagulant have been added in face before landfill, increased secondary deep dewatering intractability, another Aspect can occur the biochemical reaction of complexity in landfill sludge in anaerobic environment, and moisture content can increase again, and sludge components become It is more complicated.For landfill municipal sludge characteristic, the present invention design curing agent include carbide slag, sulphate aluminium cement, miberal powder, Flyash and molysite, add according to certain butt sludge percentage, and in use according to certain order of addition and stirring Time is carried out, and can be effectively improved the dewatering of sludge, and structural behaviour, water the reason characteristic to sludge, physical and mechanical property enter Row conditioning, makes the de- steady, flocculation of the colloidal solid in sludge, sloughs large quantity of moisture, is that the deep dehydration of sludge builds basic condition, Moisture content of the cake can be down to 50%-60% after dehydration.The present invention solves the problems, such as to have filled municipal sludge deep dehydration, dehydration Sludge can make greening soil, compost disposal, brickmaking, haydite etc..Curing agent is easily obtained and cheap.With reference to specific reality The present invention is described in further detail to apply example.
The landfill municipal sludge in certain Sludge landfill area is taken, moisture content is 80%, butt quality is 16kg, is poured into conditioning In homogenizing bucket.After carbide slag is dissolved, add under agitation, stir 5-10min, the carbide slag is special purchased from Shanghai Pujiang Plant gas Co., Ltd;Sulphate aluminium cement is subsequently added into, 3-5min is stirred, the sulphate aluminium cement is purchased from Yicheng An Date Plant Cement Co., Ltd;Miberal powder is added afterwards, 3-5min is stirred, and the miberal powder is purchased from Hebei Ke Xu building materials Co., Ltd;Again plus Enter flyash, stir 5-8min, flyash is three-level ash, purchased from new energy Development Co., Ltd of Yangzhou China Telecom.;It is eventually adding three Ferric chloride solution, mass fraction is 38%, purchased from Shanghai Huan Fa Chemical Co., Ltd.s, will be adjusted in homogenizing bucket after stirring 10-15min Sludge after reason is pumped into and carry out in compact board frame pressure filter experiment machine press filtration, curing agent addition and by plate compression testing machine pressure Moisture content of the cake after filter is shown in Table 1.
Each embodiment curing agent addition of table 1 and moisture content of the cake
Embodiment of above is only the present invention more preferably mode, is not intended to limit the invention, all in essence of the invention Within god and principle, any modification, equivalent substitution and improvements made etc. should be included within the scope of the present invention.

Claims (2)

1. one kind has filled municipal sludge curing agent, it is characterised in that the curing agent comprising carbide slag, sulphate aluminium cement, Miberal powder, flyash and molysite, each component is respectively relative to the ratio between sludge butt in the curing agent:
Carbide slag:37.5%-62.5%;
Flyash:6.25%-12.5%;
Sulphate aluminium cement:12.5%-25%;
Miberal powder:6.25%-12.5%;
Molysite:2.75%-3.25%;
Above-mentioned sludge butt refers to the quality of over dry sludge in wet mud.
2. a kind of deep dehydration method for having filled municipal sludge curing agent according to claim 1, it is characterised in that bag Include following steps:
(1) after carbide slag first being dissolved in into water, add under agitation, stir 5-10min.
(2) sulphate aluminium cement is subsequently added into, 3-5min is stirred.
(3) miberal powder is added after, 3-5min is stirred.
(4) flyash is added, 5-8min is stirred.
(5) molysite is eventually adding, 10-15min is stirred.
CN201710137689.6A 2017-03-09 2017-03-09 One kind has filled municipal sludge curing agent and its deep dehydration method Pending CN106865926A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710137689.6A CN106865926A (en) 2017-03-09 2017-03-09 One kind has filled municipal sludge curing agent and its deep dehydration method

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Application Number Priority Date Filing Date Title
CN201710137689.6A CN106865926A (en) 2017-03-09 2017-03-09 One kind has filled municipal sludge curing agent and its deep dehydration method

Publications (1)

Publication Number Publication Date
CN106865926A true CN106865926A (en) 2017-06-20

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111606547A (en) * 2020-04-17 2020-09-01 路德环境科技股份有限公司 Municipal sludge treatment method and equipment
CN112159052A (en) * 2020-09-24 2021-01-01 广州珠科院工程勘察设计有限公司 Quick dehydration curing agent
CN113149377A (en) * 2021-02-09 2021-07-23 虞克夫 Dewatered sludge curing agent, preparation method and use method

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101638311A (en) * 2009-07-10 2010-02-03 北京古华建业淤泥固化科技有限公司 Slit and sludge curing agent
CN102424511A (en) * 2011-09-02 2012-04-25 重庆大学 Solidification treatment method for sludge of urban sewage plant
KR101418053B1 (en) * 2012-12-21 2014-07-09 주식회사 포스코 Coal briquettes and method for manufacturing the same
CN105254166A (en) * 2015-11-14 2016-01-20 辽宁工程技术大学 Dewatered sludge curing agent and preparing method and using method thereof
CN105601063A (en) * 2016-01-19 2016-05-25 赵东星 Sludge solidifying agent for treating sludge in river channels and method for preparing sludge solidifying agent
CN105801056A (en) * 2016-04-13 2016-07-27 吴申龙 Efficient curing agent for treating sewer sludge and preparation method of efficient curing agent
CN105923951A (en) * 2016-06-21 2016-09-07 四川新开元环保工程有限公司 Activated sludge stabilizing treatment method for sewage treatment
CN106007324A (en) * 2016-07-06 2016-10-12 无锡市华东电力设备有限公司 Solidification and desiccation process of sludge

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101638311A (en) * 2009-07-10 2010-02-03 北京古华建业淤泥固化科技有限公司 Slit and sludge curing agent
CN102424511A (en) * 2011-09-02 2012-04-25 重庆大学 Solidification treatment method for sludge of urban sewage plant
KR101418053B1 (en) * 2012-12-21 2014-07-09 주식회사 포스코 Coal briquettes and method for manufacturing the same
CN105254166A (en) * 2015-11-14 2016-01-20 辽宁工程技术大学 Dewatered sludge curing agent and preparing method and using method thereof
CN105601063A (en) * 2016-01-19 2016-05-25 赵东星 Sludge solidifying agent for treating sludge in river channels and method for preparing sludge solidifying agent
CN105801056A (en) * 2016-04-13 2016-07-27 吴申龙 Efficient curing agent for treating sewer sludge and preparation method of efficient curing agent
CN105923951A (en) * 2016-06-21 2016-09-07 四川新开元环保工程有限公司 Activated sludge stabilizing treatment method for sewage treatment
CN106007324A (en) * 2016-07-06 2016-10-12 无锡市华东电力设备有限公司 Solidification and desiccation process of sludge

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
朱英等: "《污泥循环卫生填埋技术》", 31 May 2010, 冶金工业出版社 *
王仲旭等: "《污水治理技术与运行管理》", 31 January 2015, 中国环境出版社 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111606547A (en) * 2020-04-17 2020-09-01 路德环境科技股份有限公司 Municipal sludge treatment method and equipment
CN112159052A (en) * 2020-09-24 2021-01-01 广州珠科院工程勘察设计有限公司 Quick dehydration curing agent
CN113149377A (en) * 2021-02-09 2021-07-23 虞克夫 Dewatered sludge curing agent, preparation method and use method

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