CN110526550B - Deep dehydration medicament for solid-phase sludge - Google Patents

Deep dehydration medicament for solid-phase sludge Download PDF

Info

Publication number
CN110526550B
CN110526550B CN201910773624.XA CN201910773624A CN110526550B CN 110526550 B CN110526550 B CN 110526550B CN 201910773624 A CN201910773624 A CN 201910773624A CN 110526550 B CN110526550 B CN 110526550B
Authority
CN
China
Prior art keywords
solid
percent
phase sludge
agent
dehydration
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.)
Active
Application number
CN201910773624.XA
Other languages
Chinese (zh)
Other versions
CN110526550A (en
Inventor
周继柱
梁远
颜莹莹
李雪怡
张少博
臧星华
刘迪
石伟杰
孙松厚
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 Hengrun Huichuang Environmental Technology Co ltd
Shenmei Technology Co Ltd
Original Assignee
Beijing Pioneer Sludge Disposal Technology Co ltd
Shenmei Technology 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 Beijing Pioneer Sludge Disposal Technology Co ltd, Shenmei Technology Co Ltd filed Critical Beijing Pioneer Sludge Disposal Technology Co ltd
Priority to CN201910773624.XA priority Critical patent/CN110526550B/en
Publication of CN110526550A publication Critical patent/CN110526550A/en
Application granted granted Critical
Publication of CN110526550B publication Critical patent/CN110526550B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

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
    • C02F11/12Treatment 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
    • C02F11/148Combined use of inorganic and organic substances, being added in the same treatment step

Abstract

The invention discloses a deep dehydration medicament for solid-phase sludge, which consists of the following substances in percentage by mass: 5 to 20 percent of inorganic flocculant, 0.1 to 1 percent of seepage drag reducer, 79 to 94 percent of curing proppant and 0.1 to 3 percent of wall breaking agent, wherein the inorganic flocculant is polyaluminium chloride, polyferric sulfate, ferric trichloride, aluminum sulfate, polyaluminium ferric silicate, the seepage drag reducer is polyethylene oxide, polydiallyldimethylammonium chloride, acrylamide/sodium acrylate/diallyl dimethylammonium chloride copolymer, humic acid and the like, the curing proppant is fly ash, diatomite, perlite and the like, and the wall breaking agent is potassium permanganate, potassium dichromate, calcium perchlorate, sodium percarbonate and the like. The dehydration medicament is suitable for secondary squeezing dehydration of solid-phase sludge with the water content of about 80 percent to below 60 percent by directly using a squeezing dehydration device such as a high-pressure belt machine, avoids the process problems of secondary dilution and the like of the solid-phase sludge, and does not contain components such as lime and the like which corrode high-temperature equipment and pollute the environment.

Description

Deep dehydration medicament for solid-phase sludge
Technical Field
The invention belongs to the technical field of sludge dewatering agents, and particularly relates to a composite agent suitable for direct deep dewatering of solid-phase sludge in the process of dewatering the solid-phase sludge by using a high-pressure belt type sludge deep dewatering machine and other devices.
Background
Sludge is a solid, semi-solid and liquid waste produced in the sewage treatment process. With the acceleration of the industrial and urbanization process and the development of the sewage treatment industry, the sewage treatment capacity and the sewage treatment degree are continuously improved, and the yield of the produced sludge is increased day by day. According to the estimation, the sludge yield generated by the municipal, industrial and landscape sewage treatment in China is over 1 hundred million tons/year at present, and the sludge treatment is the implementation guarantee for the final realization of the sewage treatment and is an important link in the field of national water treatment.
The sludge serving as a final product of water treatment has the characteristics of complex components, high water content, high organic matter content, strong hydrophilicity, high dehydration difficulty, high possibility of smelling, serious pollution and the like. The water content of the sludge is generally between 90 and 99 percent, the amount of the sludge is huge, the sludge must be dehydrated before the treatment in order to realize the final effective treatment of the sludge, and the dehydration reduction is an important link for reducing the subsequent treatment cost of the sludge and improving the treatment efficiency of the sludge. Before 2018, the common sludge dewatering standard in the water treatment industry is below 80%, the used dewatering equipment mainly comprises a belt filter press, a screw stacking machine and a centrifugal machine, the 80% sludge subsequent treatment method mainly comprises burying, and secondary pollution and resource waste are serious. With the tightening of the national environmental protection policy, the state at the end of 2018 promotes the standard upgrading of the sludge dewatering reduction, the dewatering rate index is promoted to be below 60 percent, the final treatment modes such as resource utilization, burying, burning and the like are adopted, and the used dewatering equipment is mainly a plate-and-frame filter press.
Aiming at the new sludge dewatering standard with water content of below 60% in 2018, the treatment standard of 80% dewatering equipment established before 2018 is urgent to be upgraded and upgraded, so that the market occupation ratio is high, and the market demand and the technical demand are very urgent. At present, for the technology of upgrading and upgrading the standard of 80% dehydration, the method mainly adopted is to dilute the solid-phase sludge with the water content of 80% to the water content of more than 97% by using water to form slurry, then add a sludge conditioner to carry out conditioning pretreatment, and then use a plate-and-frame filter press to carry out squeezing secondary dehydration to the water content of less than 60%. The process has the problems of complex and repeated processes of secondary dilution, dissolution and dosing and secondary squeezing of solid-phase sludge with water content of 80 percent, repeated dehydration equipment and process, low utilization efficiency, large secondary investment of plate frames and the like.
At present, some devices capable of directly performing solid-phase sludge squeezing and dewatering exist in the market, the purpose of upgrading the 80% water-containing sludge dewatering process can be realized, and after a pretreatment agent is added to the solid-phase sludge, the purpose of directly performing secondary squeezing and dewatering on the solid-phase sludge to achieve the water content of the sludge is achieved. Such as a high-pressure belt filter press dehydrator, the equipment and the technology have excellent market prospect and space. However, because no matched, special and efficient secondary dehydration matched reagent for directly pretreating solid-phase sludge exists at present, the technical requirement that the water content of the solid-phase sludge is below 60 percent can not be met by using common lime and common iron-aluminum salt reagents in a matched manner with equipment. Therefore, the application and popularization of the solid-phase sludge secondary dewatering equipment and technology in the market are greatly limited, and the technical advantages of the process design are not fully exerted. The common agents such as lime and the like can not meet the aim of directly conditioning and dehydrating solid-phase sludge to reach the standard, and simultaneously have secondary pollution, and the components of the agents such as lime and the like which have corrosion influence on high-temperature equipment and pollute the environment are not contained in the components.
Disclosure of Invention
The invention aims to solve the problems that solid-phase sludge subjected to dehydration treatment by sludge dehydration equipment such as a belt filter press, a screw stacking machine and a centrifugal machine can only reach about 80% of water content and cannot meet the technical requirements of new sludge dehydration upgrading and transformation with water content of less than 60% in 2018, and provides a deep dehydration medicament which is not required to dilute the solid-phase sludge by adding water, is directly added into the solid-phase sludge with the water content of about 80%, and is directly subjected to secondary squeezing dehydration reduction to the water content of less than 60% by using the dehydration equipment such as the belt filter press, the screw stacking machine and the centrifugal machine.
Aiming at the purposes, the deep dehydration medicament for solid-phase sludge adopted by the invention consists of the following substances in percentage by mass:
5 to 20 percent of inorganic flocculant, 0.1 to 1 percent of seepage drag reducer, 79 to 94 percent of curing proppant and 0.1 to 3 percent of wall breaking agent.
The deep dehydration medicament for the solid-phase sludge preferably comprises the following substances in percentage by mass:
8 to 15 percent of inorganic flocculant, 0.3 to 0.8 percent of seepage drag reducer, 83 to 90 percent of curing proppant and 1 to 2 percent of wall-breaking oxidant.
The inorganic flocculant is one or more of polyaluminium chloride, polyferric sulfate, ferric trichloride, aluminum sulfate and polyaluminum ferric silicate, and preferably polyaluminium chloride.
The seepage drag reducer is one or more of polyethylene oxide, polydiallyl dimethyl ammonium chloride, acrylamide/sodium acrylate/diallyl dimethyl ammonium chloride copolymer and humic acid, and preferably polydiallyl dimethyl ammonium chloride.
The solidified propping agent is one or more of fly ash, diatomite and perlite, and the perlite is preferred.
The wall breaking agent is one or more of potassium permanganate, potassium dichromate, calcium perchlorate and sodium percarbonate, preferably potassium permanganate.
The solid-phase sludge is solid-phase sludge with the water content of 80-85%, the adding amount of the dehydration medicament is 3-10% of the mass of the solid-phase sludge, the inorganic flocculant is dissolved into a solution with the mass concentration of 30-35% by water and then is mixed and added, and the wall breaking agent is dissolved into a solution with the mass concentration of 8-12% by water and then is mixed and added.
The dehydration medicament is a special solid-phase sludge dehydration medicament which is suitable for solid-phase sludge with the water content of about 80 percent after dehydration treatment of equipment such as a belt filter press, a screw stacking machine, a centrifugal machine and the like, directly carries out secondary press dehydration and upgrading to the water content of below 60 percent by adopting the original equipment, and is a special composite sludge conditioner based on the seepage drag reduction, the sludge seepage framework theory, the sludge press dehydration performance improvement theory and the like. The inorganic flocculant in the components releases gap/bound water in the sludge by utilizing the flocculation dehydration function of the inorganic flocculant; seepage flow channels among sludge micelles/groups are established by the seepage flow drag reducer and the solidified propping agent, so that the seepage flow resistance of sludge dewatering is reduced, and the dewatering efficiency is improved; the wall-breaking agent improves the surface/interface activity of the sludge micelle on the basis of oxidizing and decomposing low-molecular organic matters on the outer layer of the sludge micelle, and releases intracellular water and capillary water in the micelle after the decomposition and wall breaking.
The invention has the following beneficial effects:
1. the dehydration medicament is a novel medicament used for direct secondary dehydration of solid-phase sludge, is suitable for solid-phase sludge with the water content of 80 percent after dehydration by sludge dehydration equipment such as a belt filter press, a screw stacking machine, a centrifugal machine and the like, and is upgraded to the solid-phase sludge secondary squeezing dehydration medicament with the water content of below 60 percent by direct secondary dehydration decrement upgrading by the sludge dehydration equipment. The treatment mode belongs to an innovative treatment mode for secondary dehydration of solid-phase sludge.
2. The dehydration medicament avoids the complex and repeated processes of secondary dilution, dissolution and addition and squeezing of solid-phase sludge with water content of 80%, realizes dehydration after direct addition of chemicals to the solid-phase sludge with water content of 80%, improves the dehydration index to be below 60%, realizes upgrading transformation from direct dehydration with water content of about 80% to water content of below 60% through solid-phase sludge squeezing equipment, can fully develop and meet the market requirements on the secondary dehydration medicament and technology for the solid-phase sludge, and solves the technical problem of realizing direct squeezing equipment dehydration of the solid-phase sludge.
3. The dehydration medicament is suitable for being matched with sludge dehydration equipment such as a high-pressure belt machine and the like capable of continuously dehydrating sludge, realizes continuity and secondary direct dehydration reduction of solid-phase sludge, greatly improves the sludge treatment capacity of batches such as plate frames and the like, reduces the occupied land and realizes movable sludge emergency dehydration engineering.
4. The dehydration medicament does not contain medicament components such as lime, chlorine root substances and the like which pollute high-temperature equipment and the environment, has no negative influence on subsequent sludge resource treatment and utilization, has good environmental adaptability and simple and convenient adding operation, and can realize the direct adding of the medicament into solid sludge to realize dehydration.
Detailed Description
The present invention will be described in further detail with reference to examples, but the scope of the present invention is not limited to these examples.
Example 1
The dehydrating agent of this example consists of:
inorganic flocculant: 5g of polyaluminum chloride;
seepage drag reducer: 0.1g of polyethylene oxide;
curing the propping agent: 94.8g of fly ash;
wall breaking agent: 0.1g of potassium permanganate.
Example 2
The dehydrating agent of this example consists of:
inorganic flocculant: 20g of polyaluminum chloride;
seepage drag reducer: 1.0g of polyethylene oxide;
curing the propping agent: 76.0g fly ash;
wall breaking agent: 3.0g of potassium permanganate.
Example 3
The dehydrating agent of this example consists of:
inorganic flocculant: 10g of polyaluminum chloride;
seepage drag reducer: 0.5g of polyethylene oxide;
curing the propping agent: 89.0g of fly ash;
wall breaking agent: 0.5g of potassium permanganate.
Example 4
The dehydrating agent of this example consists of:
inorganic flocculant: 10g of polymeric ferric sulfate;
seepage drag reducer: 0.5g of polydiallyldimethylammonium chloride;
curing the propping agent: 89.0g of diatomaceous earth;
wall breaking agent: 0.5g of potassium dichromate.
Example 5
The dehydrating agent of this example consists of:
inorganic flocculant: 10g of ferric chloride;
seepage drag reducer: 0.5g acrylamide/sodium acrylate/diallyldimethylammonium chloride copolymer;
curing the propping agent: 89.0g of perlite;
wall breaking agent: 0.5g of calcium perchlorate.
Example 6
The dehydrating agent of this example consists of:
inorganic flocculant: 10g of aluminum sulfate, the mass percentage content is 10%;
seepage drag reducer: 0.5g acrylamide/sodium acrylate/diallyldimethylammonium chloride copolymer;
curing the propping agent: 89.0g of perlite;
wall breaking agent: 0.5g of sodium percarbonate.
Example 7
The dehydrating agent of this example consists of:
inorganic flocculant: 15g of aluminium sulphate;
seepage drag reducer: 0.5g acrylamide/sodium acrylate/diallyldimethylammonium chloride copolymer;
curing the propping agent: 84.0g of perlite;
wall breaking agent: 0.5g of sodium percarbonate.
Example 8
The dehydrating agent of this example consists of:
inorganic flocculant: 5g of polyaluminum ferric silicate;
seepage drag reducer: 0.5g of humic acid;
curing the propping agent: 94.0g of perlite;
wall breaking agent: 0.5g of sodium percarbonate.
Example 9
The dehydrating agent of this example consists of:
inorganic flocculant: 5g of polyaluminum chloride;
seepage drag reducer: 0.5g of humic acid;
curing the propping agent: 89.0g of perlite;
wall breaking agent: 0.5g of potassium permanganate.
In order to prove the beneficial effects of the invention, the inventor adopts the dehydration medicament of the embodiment 1-9 to carry out secondary dehydration on the solid-phase sludge with the water content of about 80 percent, and the specific method is as follows:
preparing an inorganic flocculant into an aqueous solution with the mass concentration of 33% and preparing a wall breaking agent into an aqueous solution with the mass concentration of 10%, then adding all components into the solid-phase sludge, and mechanically stirring for pretreatment for 3 min; then the pretreated solid-phase sludge enters a high-pressure belt type filter-pressing dehydrator for pressing dehydration; the pressure of the high-pressure belt type filter-press dehydrator is more than 0.2MPa, and the press dehydration time is more than 1.5 min. The test equipment yields the mud water content, and the results are shown in table 1.
TABLE 1 results of testing the dewatering performance of solid-phase sludge with different dewatering agents
Figure BDA0002174369820000061
As can be seen from Table 1, the dehydration medicament provided by the invention can meet the index requirement of below 60% after national standard extraction after being used for direct secondary squeezing dehydration of solid-phase sludge with the water content of 80-85%.

Claims (6)

1. A dehydration medicament for solid-phase sludge is characterized by comprising the following substances in percentage by mass:
5 to 20 percent of inorganic flocculant, 0.1 to 1 percent of seepage drag reducer, 79 to 94 percent of curing proppant and 0.1 to 3 percent of wall breaking agent;
the inorganic flocculant is one or more of polyaluminium chloride, polyferric sulfate, ferric trichloride, aluminum sulfate and polyaluminium ferric silicate;
the seepage drag reducer is one or more of polyethylene oxide, polydiallyl dimethyl ammonium chloride, acrylamide/sodium acrylate/diallyl dimethyl ammonium chloride copolymer and humic acid;
the solidified propping agent is one or more of fly ash, diatomite and perlite;
the wall breaking agent is one or more of potassium permanganate, potassium dichromate, calcium perchlorate and sodium percarbonate,
the solid-phase sludge is solid-phase sludge with the water content of 80-85 percent,
the adding amount of the dehydration medicament is 3-10% of the mass of the solid-phase sludge, wherein the inorganic flocculant is mixed and added after being dissolved into a solution with the mass concentration of 30-35% by water, the wall-breaking agent is mixed and added after being dissolved into a solution with the mass concentration of 8-12% by water,
the solid-phase sludge treated by the dehydrating agent is directly subjected to secondary squeezing dehydration by a belt filter press, a screw stacking machine or a centrifugal machine to reduce the water content to below 60 percent.
2. The dewatering agent for solid-phase sludge according to claim 1, characterized in that the dewatering agent consists of the following substances in percentage by mass:
8 to 15 percent of inorganic flocculant, 0.3 to 0.8 percent of seepage drag reducer, 83 to 90 percent of curing proppant and 1 to 2 percent of wall-breaking oxidant.
3. The dewatering agent for solid-phase sludge according to claim 2, characterized in that: the inorganic flocculant is polyaluminium chloride.
4. The dewatering agent for solid-phase sludge according to claim 2, characterized in that: the seepage drag reducer is poly diallyl dimethyl ammonium chloride.
5. The dewatering agent for solid-phase sludge according to claim 2, characterized in that: the solidified propping agent is perlite.
6. The dewatering agent for solid-phase sludge according to claim 2, characterized in that: the wall breaking agent is potassium permanganate.
CN201910773624.XA 2019-08-21 2019-08-21 Deep dehydration medicament for solid-phase sludge Active CN110526550B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910773624.XA CN110526550B (en) 2019-08-21 2019-08-21 Deep dehydration medicament for solid-phase sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910773624.XA CN110526550B (en) 2019-08-21 2019-08-21 Deep dehydration medicament for solid-phase sludge

Publications (2)

Publication Number Publication Date
CN110526550A CN110526550A (en) 2019-12-03
CN110526550B true CN110526550B (en) 2022-05-03

Family

ID=68662325

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910773624.XA Active CN110526550B (en) 2019-08-21 2019-08-21 Deep dehydration medicament for solid-phase sludge

Country Status (1)

Country Link
CN (1) CN110526550B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111204824A (en) * 2020-01-17 2020-05-29 广东东日环保股份有限公司 River surge sewage treatment agent and preparation method thereof
CN111056729B (en) * 2020-02-18 2022-06-28 广州绿邦环境技术有限公司 Medicament for sludge filter pressing and production process
CN111718104A (en) * 2020-06-19 2020-09-29 中碳(上海)科技有限公司 Polysilicate iron chemical conditioner and preparation method thereof

Family Cites Families (24)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52101669A (en) * 1976-02-21 1977-08-25 Ishikawajima Harima Heavy Ind Co Ltd Treatment of sludge by solidifying
JPS5518209A (en) * 1978-07-24 1980-02-08 Japan Organo Co Ltd Harmless disposal of cyanogen containing sludge
JPS57180500A (en) * 1981-04-30 1982-11-06 Unitika Ltd Dehydration treatment for organic sludge
CN101224912B (en) * 2008-01-25 2011-03-23 广州普得环保设备有限公司 Method for drying sludge
CN101475411B (en) * 2009-02-10 2012-09-05 成都禾力宝生物肥料有限责任公司 Solid phase sludge joint treatment method and use
WO2011119753A2 (en) * 2010-03-23 2011-09-29 University Of Utah Research Foundation Methods for deactivating biomass
CN101838097B (en) * 2010-04-08 2011-11-30 赵润林 Sludge drying agent and preparation method and using method thereof
CN102303944B (en) * 2011-08-22 2014-08-27 广州新致晟环保科技机械设备有限公司 Method for re-treating dewatered sludge
CN102815851A (en) * 2012-08-07 2012-12-12 上海交大辛德环保有限公司 Depth sludge drying regulation system, and method thereof
CN102964041B (en) * 2012-12-03 2014-02-12 厦门荣惠盛新材料有限公司 Sludge burning treatment device and burning treatment method using device
CN103073166B (en) * 2013-02-05 2014-10-22 上海市环境科学研究院 Method for simultaneously stabilizing heavy metals and deeply dewatering municipal sludge for municipal sludge
CN103951146B (en) * 2014-03-14 2015-11-18 上海申耀环保工程有限公司 A kind of mud decrement and mummification method for combined use
CN204281535U (en) * 2014-11-30 2015-04-22 太原科技大学 A kind of modified dewatering system of environment-friendly type compound of municipal sludge
CN104556621B (en) * 2015-01-16 2018-08-17 光大环保技术研究院(深圳)有限公司 A kind of method for sludge treatment
CN104724897A (en) * 2015-03-25 2015-06-24 广东粤科环保科技有限公司 Sludge dewatering conditioning agent and use method thereof
CN105016601A (en) * 2015-07-03 2015-11-04 天津霍普环保科技有限公司 Electro-osmotic dewatering technology for biological sludge
CN105417925A (en) * 2015-12-28 2016-03-23 山东大学 Preparation method of sludge conditioning agent for deep dehydration of sludge
CN106219941A (en) * 2016-09-05 2016-12-14 东江环保股份有限公司 The method of resource of hydrogen is produced in municipal sludge deep dehydration and the pyrolysis of mud cake steam gasification
CN106396316A (en) * 2016-12-05 2017-02-15 上海申耀环保工程有限公司 Sludge curing agent as well as preparation method and use method thereof
CN106587571A (en) * 2016-12-30 2017-04-26 西华大学 Method for co-conditioning of sludge through multiple types of agents
CN107686225A (en) * 2017-09-05 2018-02-13 神美科技有限公司 A kind of compound type sludge conditioner for sludge dewatering
CN109179955A (en) * 2018-08-14 2019-01-11 辽宁中绿环境工程有限公司 A kind of sludge dewatering treatment system and its processing method
CN109336353B (en) * 2018-12-07 2020-01-14 杭州萧山环境投资发展有限公司 Online conditioning method for deep dehydration of sludge
CN109928603B (en) * 2019-04-23 2021-06-29 同济大学 Preparation method and use method of green sludge dewatering agent

Also Published As

Publication number Publication date
CN110526550A (en) 2019-12-03

Similar Documents

Publication Publication Date Title
CN110526550B (en) Deep dehydration medicament for solid-phase sludge
CN102992553B (en) Method for comprehensively treating and utilizing dissolving pulp black liquor
CN1986788B (en) Sludge dewatering chemical amendment and its dewatering method
CN102674657A (en) Sludge dewatering method for urban sewage plant
CN102603152A (en) Sludge deep dehydration conditioning agent and application thereof
CN106746482A (en) The compound conditioner of sludge dewatering and mud dewatering method
CN109485230B (en) Deep dehydration pretreatment process for landfill sludge
CN106830621B (en) Composite sludge dehydrating agent and preparation method and application thereof
CN105000786A (en) Drug and treatment process for deep dehydration on sludge
CN111018311A (en) Normal-temperature modified sludge dehydrating agent and preparation method thereof
CN104261652A (en) Efficient sludge dewatering flocculant
CN103113013A (en) Compound type sludge dewatering conditioner and application method thereof
CN107162383B (en) High-efficiency low-chlorine conditioner and application thereof in dehydration of high-solid digested sludge
CN102432152A (en) Method for pretreating and strengthening sludge dehydration by using acetylene sludge
CN103241922B (en) Compounded sludge dewatering conditioner and application and method thereof
CN112624565B (en) Polyhydroxy organic cation polymer sludge conditioner for deep dehydration of sludge and preparation method thereof
CN103466915B (en) For composition and the dewatering of municipal sludge deep dehydration
CN113683279A (en) Dehydration method of thermal hydrolysis anaerobic digestion sludge
CN106587296A (en) Bamboo pulp cellulose based flocculation decolorization composite functional material and preparation method thereof
CN101381136A (en) High-efficiency broadspectrum flocculant and preparation method thereof
CN115959814B (en) Organic sludge conditioner for improving mechanical properties of mud cakes and sludge dewatering method
CN104788001A (en) Sludge high-dry dehydration conditioning method
CN114702229A (en) Compound municipal sludge improvement agent and preparation method and application thereof
CN109650697B (en) Pretreatment method for plate-frame filter pressing of bloom-forming cyanobacteria
CN203382630U (en) Sludge treatment system

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right

Effective date of registration: 20230613

Address after: Room 4119, 1f, building 4, Xindu Hotel, 21 Chegongzhuang street, Xicheng District, Beijing 100037

Patentee after: Beijing Hengrun Huichuang Environmental Technology Co.,Ltd.

Patentee after: SHENMEI TECHNOLOGY CO.,LTD.

Address before: 21 Chegongzhuang st, Xicheng District, Beijing

Patentee before: Beijing Pioneer Sludge Disposal Technology Co.,Ltd.

Patentee before: SHENMEI TECHNOLOGY CO.,LTD.

TR01 Transfer of patent right