[go: up one dir, main page]

CN100497415C - Cationic dehydrating agent preparation method - Google Patents

Cationic dehydrating agent preparation method Download PDF

Info

Publication number
CN100497415C
CN100497415C CNB2005100475425A CN200510047542A CN100497415C CN 100497415 C CN100497415 C CN 100497415C CN B2005100475425 A CNB2005100475425 A CN B2005100475425A CN 200510047542 A CN200510047542 A CN 200510047542A CN 100497415 C CN100497415 C CN 100497415C
Authority
CN
China
Prior art keywords
accordance
initiator
cationic
mol
persulphate
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
CNB2005100475425A
Other languages
Chinese (zh)
Other versions
CN1955125A (en
Inventor
王有华
杨丽
赵景霞
黄玉洪
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.)
China Petroleum and Chemical Corp
Sinopec Fushun Research Institute of Petroleum and Petrochemicals
Original Assignee
China Petroleum and Chemical Corp
Sinopec Fushun Research Institute of Petroleum and Petrochemicals
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 China Petroleum and Chemical Corp, Sinopec Fushun Research Institute of Petroleum and Petrochemicals filed Critical China Petroleum and Chemical Corp
Priority to CNB2005100475425A priority Critical patent/CN100497415C/en
Publication of CN1955125A publication Critical patent/CN1955125A/en
Application granted granted Critical
Publication of CN100497415C publication Critical patent/CN100497415C/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Addition Polymer Or Copolymer, Post-Treatments, Or Chemical Modifications (AREA)
  • Treatment Of Sludge (AREA)

Abstract

A cationic dewatering agent for treating sewage or sludge is prepared from acrylamide, methylacrolyloxyethyl ammonium chloride and deionized water through polymerizing reaction in solution under the action of trigger, granulating, drying and pulverizing.

Description

A kind of preparation method of cationic dehydrating agent
Technical field
The present invention relates to a kind of preparation method of cationic dehydrating agent, particularly in oil, the chemical industry production process, the oily sludge that is produced is handled the preparation method of the cationic dehydrating agent of usefulness.
Background technology
Oily sludge mainly results from oil field and refinery, and as in dehydrating of crude oil, there are a large amount of oily sludges in bottoms such as water knockout, storage tanker and slop oil tank; In the oil field, also there are a large amount of oily sludges in the oil trap in the sewage-farm of refinery, flotation cell, aeration tank etc.The composition of these mud is very complicated, generally forms by oil-in-water (O/W), water-in-oil (W/O) and suspended solids, and fully emulsified, viscosity is bigger, is difficult to sedimentation.Because the technological process difference that oily sludge produces, its oil-containing, moisture difference are bigger, and wherein oil is made up of hundreds of dissimilar organic compound, and majority is poisonous and harmful and is difficult to biodegradable material.Solid particulate in mud, is emulsified state Gu oil-water-three mixes with minimum particle distribution in the oily sludge, and environment is had great hazardness.
Carrying out processed before the final processing of mud is absolutely necessary.The effect of dewatering agent be exactly in and the electric charge of solid particles band, the net connection is built bridge, condense thereby make between the molecule of mud, finally become macrobead, thereby improve its solid-liquid separation performance.In recent years, organic polymer coargulator development has wide in varietyly rapidly, and consumption is few, and it is few to give birth to slag, is easy to solid-liquid separation and reduces advantage such as equipment corrosion, occupies more and more important position in water treatment field.Disclosed a kind of cationic high-molecular flocculant as Chinese patent CN1247838A, it is that to adopt polyacrylamide, formaldehyde, dimethylamine be main raw, reacts the colloid of the amine methyl polyacrylamide that obtains now by Manny.There are shortcomings such as the loaded down with trivial details and flocculation agent effective content that obtain of technological process is low in this method.CN1305976A has disclosed a kind of treatment process of mud.It is to adopt in mud behind the adding ferrous sulfate, add the cationic-type polyacrylamide flocculation agent again, and the mud after will flocculating to pass through pressure-filtering separating machine.Through behind the isolating clod natural air drying, pulverize with Universalpulverizer, and after adding a certain amount of nitrogen, phosphorus, potash fertilizer therein, as fertilizer sources uses.This method can cause secondary environmental pollution.CN1248173A is used in combination with cationic polymer flocculent or inorganic flocculating agent with sulfonated styrene polymer and/or its salt, as sludge dehydrating agent.CN1464887A is a dewatering agent with the modifier of polyalkyleneimine, is mainly used in the paper making raw material pretreating reagent.The dewatering of above-mentioned dewatering agent needs further to improve.Chinese patent CN1336391A has disclosed a kind of cationic flocculant, and it is that to adopt inorganic ammonium salt, alkanoic, Dicyanodiamide be main raw, obtains through polycondensation.The flocculating agent molecule amount that this method obtains is lower, shortcomings such as flocculation bridge formation ability.
Summary of the invention
At the deficiencies in the prior art, the invention provides a kind of preparation method of cationic dehydrating agent, when the product of preparation is used for the oily sludge processing, can remove the interstitial water in the mud effectively, the conglobation property of filter cake is good, thereby improves the dehydrating effect of mud.Use cationic dehydrating agent of the present invention to carry out sludge treatment, its filter back liquid COD is lower than 1000mg/L substantially, and oil-contg is below 100mg/L.
The cationic dehydrating agent of the present invention's preparation is the multipolymer of cationic monomer methylacryoyloxyethyl trimethyl ammonium chloride and acrylamide monomer:
Contain structural unit A in the multipolymer:
Figure C200510047542D00051
With structural unit B:
Figure C200510047542D00052
The mol ratio of structural unit A and structural unit B is 30:1~1:30 in the multipolymer, preferred 25:1~1:25, the limiting viscosity 900cm of multipolymer 3/ g~1600cm 3/ g, cationic degree 0.3mmol/g~1.2mmol/g.
The preparation process of cationic dehydrating agent of the present invention is as follows:
In the required ratio of cationic dehydrating agent polymer monomers, acrylamide monomer and cationic monomer methylacryoyloxyethyl trimethyl ammonium chloride monomer are added in the deionized water, nitrogen blowing is removed dissolved oxygen, adds initiator at last, auxiliary agent carries out polyreaction.After question response is complete,, promptly get this dewatering agent through extruding pelletization, drying, pulverizing.
The monomeric polymerization proportioning of acrylamide monomer and methylacryoyloxyethyl trimethyl ammonium chloride (mol ratio) is, acrylamide: methylacryoyloxyethyl trimethyl ammonium chloride=30:1~1:30 (mol ratio), best polymerization proportioning is: acrylamide: methylacryoyloxyethyl trimethyl ammonium chloride=25:1~1:25 (mol ratio); The total concn of monomer polymerization is: 0.5mol/L~5.0mol/L, and best polymerization concentration is: 0.8mol/L~4.5mol/L; The polymeric temperature of reaction is: 20 ℃~60 ℃, optimum temps is: 30 ℃~60 ℃; Polymerization reaction time is 1h~8h, preferably 3h~6h.
Polymerization process adopts different initiator systems, carries out free radical copolymerization.Initiator is one or both of water-soluble azo initiator and redox initiator.The add-on of initiator is 10 -5Mol/L~10 -2Mol/L, optimal addn is: 5 * 10 -5Mol/L~5 * 10 -3Mol/L.Redox initiator is one or both of persulphate and sulphite, and wherein, the proportioning of persulphate and sulphite is: 1:0.1~1 (weight ratio), best proportioning are 1:0.5~1 (weight ratio).Wherein persulphate is one or more in Potassium Persulphate, ammonium persulphate and the Sodium Persulfate; Sulphite is one or more in S-WAT, sodium bisulfite, potassium sulfite, Potassium hydrogen sulfite, ammonium sulphite and the ammonium bisulfite; Water-soluble azo initiator is a water-soluble azo class thing, as N, and one or more in N-dihydroxy ethyl azo-bis-isobutyrate hydrochloride, the two amidine propane dihydrochlorides of azo, two (2-methyl, 2-amidine propane)-hydrochlorides of 2,2-azo.
Auxiliary agent is one or more of edta and its sodium salt, ethylene diaminetetraacetic acid and sodium salt thereof, diethylenediamine pentaacetic acid and sodium salt thereof.The add-on of auxiliary agent is 10 of a polymerization single polymerization monomer total amount -5G/g~10 -2G/g.
The polyreaction of sludge dehydrating agent preparation process of the present invention is controlled easily, and is easy and simple to handle, and the reaction times is shorter, and whole technological process only needs 6h~8h to finish.When particularly adopting persulphate and sulphite composite initiator, can carry out polyreaction under lower temperature, polymerization process is easy to control.This cationic dehydrating agent can be applied in sewage, the sludge treatment of industries such as oil, petrochemical industry, chemical industry, light industry.Sludge dehydrating agent of the present invention can be removed the interstitial water in the mud effectively when handling various sludge dewatering treatment, the conglobation property of filter cake is good, thereby improves the dehydrating effect of mud.Use cationic dehydrating agent of the present invention to carry out sludge treatment, its filter back liquid COD is lower than 1000mg/L substantially, and oil-contg is below 100mg/L.
Embodiment
Further specify the preparation method and the result of use of sludge dehydrating agent of the present invention below in conjunction with embodiment.
Embodiment 1
To be equipped with in the four-hole boiling flask of 1000ml of thermometer, filling tube, import and export of nitrogen, add acrylamide monomer 116.3g, cationic monomer methylacryoyloxyethyl trimethyl ammonium chloride 44.6g, disodium ethylene diamine tetraacetate (chemical pure) 0.45g, deionized water 500ml, nitrogen blowing is removed dissolved oxygen, adds N at last, N-dihydroxy ethyl azo-bis-isobutyrate hydrochloride initiator 10 -4Mol/L adds ammonium persulphate (chemical pure) 0.3g, and sodium bisulfite (chemical pure) 0.3g in 40 ℃ of water-baths, carried out copolymerization 4 hours.Question response with its extruding pelletization, drying, pulverizing, promptly gets dewatering agent-1 after finishing.
Embodiment 2
To be equipped with in the four-hole boiling flask of 1000ml of thermometer, filling tube, import and export of nitrogen, add acrylamide monomer 96.9g, cationic monomer methylacryoyloxyethyl trimethyl ammonium chloride 33.8g, disodium ethylene diamine tetraacetate (chemical pure) 0.38g, deionized water 500ml, nitrogen blowing is removed dissolved oxygen, adds N at last, N-dihydroxy ethyl azo-bis-isobutyrate hydrochloride initiator 5 * 10 -4Mol/L adds ammonium persulphate (chemical pure) 0.5g, and sodium bisulfite (chemical pure) 0.4g in 35 ℃ of water-baths, carried out copolymerization 6 hours.Question response with its extruding pelletization, drying, pulverizing, promptly gets dewatering agent-2 after finishing.
Embodiment 3
To be equipped with in the four-hole boiling flask of 1000ml of thermometer, filling tube, import and export of nitrogen, add acrylamide monomer 131.3g, cationic monomer methylacryoyloxyethyl trimethyl ammonium chloride 25.3g, disodium ethylene diamine tetraacetate (chemical pure) 0.55g, deionized water 500ml, nitrogen blowing is removed dissolved oxygen, adds N at last, N-dihydroxy ethyl azo-bis-isobutyrate hydrochloride initiator 10 -4Mol/L adds ammonium persulphate (chemical pure) 0.35g, in 55 ℃ of water-baths, carries out copolymerization 5 hours.Question response with its extruding pelletization, drying, pulverizing, promptly gets dewatering agent-3 after finishing.
Embodiment 4
To be equipped with in the four-hole boiling flask of 1000ml of thermometer, filling tube, import and export of nitrogen, add acrylamide monomer 87.5g, cationic monomer methylacryoyloxyethyl trimethyl ammonium chloride 18.5g, disodium ethylene diamine tetraacetate (chemical pure) 0.4g, deionized water 500ml, nitrogen blowing is removed dissolved oxygen, add ammonium persulphate (chemical pure) 0.6g at last, sodium bisulfite (chemical pure) 0.5g in 30 ℃ of water-baths, carried out copolymerization 5 hours.Question response with its extruding pelletization, drying, pulverizing, promptly gets dewatering agent-4 after finishing.
Embodiment 5
To be equipped with in the four-hole boiling flask of 1000ml of thermometer, filling tube, import and export of nitrogen, add acrylamide monomer 16.5g, cationic monomer methylacryoyloxyethyl trimethyl ammonium chloride 118.5g, disodium ethylene diamine tetraacetate (chemical pure) 0.4g, deionized water 500ml, nitrogen blowing is removed dissolved oxygen, adds N at last, N-dihydroxy ethyl azo-bis-isobutyrate hydrochloride initiator 5 * 10 -4Mol/L, ammonium persulphate (chemical pure) 0.3g, sodium bisulfite (chemical pure) 0.25g in 50 ℃ of water-baths, carried out copolymerization 5 hours.Question response with its extruding pelletization, drying, pulverizing, promptly gets dewatering agent-5 after finishing.
Each embodiment obtains dewatering agent product index such as table 1.
Each embodiment of table 1 obtains the dewatering agent product index
Index Dewatering agent-1 Dewatering agent-2 Dewatering agent-3 Dewatering agent-4 Dewatering agent-5
Limiting viscosity cm 3/g 1590 1475 1195 1420 968
Cationic degree mmol/g 0.32 0.71 0.44 0.86 0.95
Embodiment 6
Get certain refinery oily sludge and carry out the breakdown of emulsion floc test.
Table 2 is handled certain refinery oily sludge laboratory evaluation result
Annotate: ZDMC is the multipolymer of acrylamide and dimethyl diallyl ammonium chloride, limiting viscosity 430mm 2/ s, cationic degree 0.3mmol/g.

Claims (11)

1, a kind of preparation method of cationic dehydrating agent, its feature comprises following process in preparation process: in the required ratio of cationic dehydrating agent polymer monomers, acrylamide monomer and cationic monomer methylacryoyloxyethyl trimethyl ammonium chloride monomer are added in the deionized water, nitrogen blowing is removed dissolved oxygen, adds initiator at last, auxiliary agent carries out polyreaction; After question response is complete,, promptly get dewatering agent through extruding pelletization, drying, pulverizing; The monomeric polymerization mol ratio of described acrylamide monomer and cationic monomer methylacryoyloxyethyl trimethyl ammonium chloride is acrylamide: methylacryoyloxyethyl trimethyl ammonium chloride=30:1~1:30; Described initiator is water-soluble azo initiator and redox initiator.
2, in accordance with the method for claim 1, it is characterized in that described monomeric total concn is: 0.5mol/L~5.0mol/L.
3, in accordance with the method for claim 1, it is characterized in that described monomeric total concn is 0.8mol/L~4.5mol/L.
4, in accordance with the method for claim 1, it is characterized in that the polymeric temperature of reaction is: 20 ℃~60 ℃, polymerization reaction time is 1h~8h.
5, in accordance with the method for claim 1, the add-on that it is characterized in that described initiator is 10 -5Mol/L~10 -2Mol/L.
6, in accordance with the method for claim 1, it is characterized in that described redox initiator is one or both of persulphate and sulphite.
7, in accordance with the method for claim 6, it is characterized in that described persulphate is one or more in Potassium Persulphate, ammonium persulphate and the Sodium Persulfate; Sulphite is one or more in S-WAT, sodium bisulfite, potassium sulfite, Potassium hydrogen sulfite, ammonium sulphite and the ammonium bisulfite.
8, in accordance with the method for claim 1, it is characterized in that described water-soluble azo initiator is a water-soluble azo class thing.
9, in accordance with the method for claim 1, it is characterized in that described initiator add-on is: 5 * 10 -5Mol/L~5 * 10 -3Mol/L.
10, in accordance with the method for claim 1, it is characterized in that described auxiliary agent is one or more of edta and its sodium salt, ethylene diaminetetraacetic acid and sodium salt thereof, diethylenediamine pentaacetic acid and sodium salt thereof, the add-on of auxiliary agent is 10 of a polymerization single polymerization monomer total amount -5G/g~10 -2G/g.
11, in accordance with the method for claim 6, the weight ratio that it is characterized in that described persulphate and sulphite is: 1:0.1~1.
CNB2005100475425A 2005-10-26 2005-10-26 Cationic dehydrating agent preparation method Active CN100497415C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNB2005100475425A CN100497415C (en) 2005-10-26 2005-10-26 Cationic dehydrating agent preparation method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNB2005100475425A CN100497415C (en) 2005-10-26 2005-10-26 Cationic dehydrating agent preparation method

Publications (2)

Publication Number Publication Date
CN1955125A CN1955125A (en) 2007-05-02
CN100497415C true CN100497415C (en) 2009-06-10

Family

ID=38062723

Family Applications (1)

Application Number Title Priority Date Filing Date
CNB2005100475425A Active CN100497415C (en) 2005-10-26 2005-10-26 Cationic dehydrating agent preparation method

Country Status (1)

Country Link
CN (1) CN100497415C (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108654143A (en) * 2018-07-11 2018-10-16 四川浩珑科技有限公司 A kind of refinery oily waste water degreaser and preparation method thereof

Families Citing this family (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101522581B (en) * 2006-10-24 2012-06-13 Mt奥科高分子株式会社 Processes for dewatering digested sewage sludge
CN101130938B (en) * 2007-09-28 2010-05-19 上海东升新材料有限公司 Cationic polymer for papermaking and preparing method thereof
CN102502705B (en) * 2011-11-02 2013-06-19 四川鸿康药物化学有限公司 Ammonium chloride fluid loss agent and preparation method thereof
CN102898580B (en) * 2012-10-29 2014-10-29 余荣和 Method for preparing polyacrylamide
CN105084711A (en) * 2014-04-25 2015-11-25 索里思科技开曼公司 Sludge dewatering
JP6737439B2 (en) * 2017-03-14 2020-08-12 栗田工業株式会社 Sludge dewatering agent and sludge dewatering method
CN109970313A (en) * 2017-12-14 2019-07-05 湖南军信环保股份有限公司 For the dehydrating and conditioning agent of thermophilic digestion sludge and the dewatering of thermophilic digestion sludge
CN108640484B (en) * 2018-05-31 2020-12-22 东莞市顶盛环保科技有限公司 Preparation method of sludge dehydrating agent
CN112759228A (en) * 2020-12-29 2021-05-07 上海丰信环保科技有限公司 Special compound polymer agent for dehydration of oily sludge of meal waste water

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108654143A (en) * 2018-07-11 2018-10-16 四川浩珑科技有限公司 A kind of refinery oily waste water degreaser and preparation method thereof

Also Published As

Publication number Publication date
CN1955125A (en) 2007-05-02

Similar Documents

Publication Publication Date Title
CN100518879C (en) Wastewater treating agent, method for wastewater treatment, sludge dehydrant and method for sludge treatment
CN101249996B (en) Organic high polymer coagulant preparation method
Li et al. UV-initiated polymerization of acid-and alkali-resistant cationic flocculant P (AM-MAPTAC): synthesis, characterization, and application in sludge dewatering
EP1274652B1 (en) Method of clarifying water using low molecular weight cationic dispersion polymers
JP6378342B2 (en) Organic wastewater treatment method
CN104085971A (en) Compound cationic flocculant and preparation method thereof
CN100497415C (en) Cationic dehydrating agent preparation method
CN104245763A (en) New cationic polymers
WO1997018167A1 (en) High performance polymer flocculating agents
CN114524904B (en) Flocculating agent for landfill leachate and preparation method thereof
JP5649279B2 (en) Dewatering method for sewage digested sludge
JP6131465B2 (en) Sludge dewatering method
US20030042209A1 (en) Polymeric flocculant and method of sludge dehydration
CN102642904B (en) Flocculating agent for treating papermaking waste water and preparation method thereof
WO2001027173A1 (en) Cationic latex terpolymers for wastewater treatment
CN1233569C (en) Cation type polymer flocculating agent and its preparation method
CN106103516A (en) Structurized block copolymer
CN101143743B (en) Method for preparing cation type polymeric flocculant
CN109553170B (en) Inorganic-organic composite polymer dephosphorization flocculant and preparation method thereof
CN100579623C (en) Method for preparing composite sludge dehydrant
CN104877070A (en) Preparation method of dried cationic polyacrylamide powder
CN101618937A (en) Hydrophobic cation polymeric flocculant and preparation method and application thereof
Sun et al. Synthesis, Characterization and Floculating Properties of Coply (AM-DAC) in Water and Wastewater Treatment
Zhao et al. Preparations of novel flocculants and its applications in the paper-making wastewater
Akryloamidowych et al. Application of acrylamide polymers as flocculants in sewages coagulation process

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