CN104130335A - High-substituted quaternary ammonium polysaccharide bioflocculant and preparation method thereof - Google Patents

High-substituted quaternary ammonium polysaccharide bioflocculant and preparation method thereof Download PDF

Info

Publication number
CN104130335A
CN104130335A CN201410352573.0A CN201410352573A CN104130335A CN 104130335 A CN104130335 A CN 104130335A CN 201410352573 A CN201410352573 A CN 201410352573A CN 104130335 A CN104130335 A CN 104130335A
Authority
CN
China
Prior art keywords
quaternary ammonium
polysaccharide bioflocculant
bioflocculant
type polysaccharide
preparation
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
CN201410352573.0A
Other languages
Chinese (zh)
Other versions
CN104130335B (en
Inventor
庄茅
胡阳
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.)
Weihai Hanbang biological environmental protection Polytron Technologies Inc
Original Assignee
WEIHAI HANBANG BIOLOGICAL ENVIRONMENTAL PROTECTION SCIENCE & 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 WEIHAI HANBANG BIOLOGICAL ENVIRONMENTAL PROTECTION SCIENCE & TECHNOLOGY Co Ltd filed Critical WEIHAI HANBANG BIOLOGICAL ENVIRONMENTAL PROTECTION SCIENCE & TECHNOLOGY Co Ltd
Priority to CN201410352573.0A priority Critical patent/CN104130335B/en
Publication of CN104130335A publication Critical patent/CN104130335A/en
Application granted granted Critical
Publication of CN104130335B publication Critical patent/CN104130335B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The invention provides a high-substituted quaternary ammonium polysaccharide bioflocculant and a preparation method thereof. The preparation method comprises the following steps: alkalizing an aqueous solution of a raw material non-ionic bioflocculant in the presence of a certain amount of a catalyst at a certain water bath temperature through a wet process, slowly adding a certain amount of a dispersant in a dropwise manner, adding an etherifying agent, reacting for a period of time, precipitating, washing with water, washing with alcohol, drying, and grinding to prepare the quaternary ammonium polysaccharide bioflocculant with the substitution degree of 0.2-1.8. The method adopting the wet process has the advantages of good stability, simple operation, easy separation, high reaction conversion rate, high cost performance, and waste liquid recycling, and the quaternary ammonium polysaccharide bioflocculant has the advantages of non-toxicity, environmental protection, no secondary pollution and biodegradability, can be used for processing drinking water, printing and dyeing wastewater, coal washing water, mineral processing, oil refining wastewater, papermaking and chemical industry wastewater, and the like, and has substantial environmental and social benefits.

Description

A kind of high degree of substitution quaternary ammonium type polysaccharide bioflocculant and preparation method thereof
Technical field
The invention belongs to water treatment flocculant technical field, particularly a kind of high degree of substitution quaternary ammonium type polysaccharide bioflocculant and preparation method thereof.
Background technology
In at present conventional water treatment flocculant, although poly-aluminium, Polyferric Sulfate, polyacrylamide etc. have good flocculating effect, but its bring the problems such as large, the corrosion pipeline of metal residual, sludge quantity and the monomer residue of polyacrylamide in water body, caused and both domestic and externally generally paid attention to.Since 20 century 70s, the states such as U.S., day, English and India have launched the development work of chemical modification natural organic high-molecular material, wherein contain polysaccharide, protein, glycoprotein or cellulosic biological flocculant and belong to natural macromolecular material because of it, produced by microbial metabolism, there is good flocculation sediment performance, and have safe, biodegradable, to features such as environment non-secondary pollutions, more and more come into one's own.
At present, modified natural polymer material mainly divides etherificate type, esterification type and graft copolymerization, and with the morning and in the majority of research of etherificate type, etherificate type product is that the hydroxyl containing in natural macromolecular material is combined and is produced by etherification reaction with etherifying agent, most widely used etherifying agent is mainly 3-chloro-2-hydroxypropyl-trimethyl ammonium chloride and 2 at present, 3-epoxypropyltrimethylchloride chloride, this etherifying agent has high reactivity, in high purity and reaction, by product is few, the features such as technological operation is simple, can with starch, Mierocrystalline cellulose, chitosan, the reactions such as guar gum, produce multiple product.The modified natural polymer flocculation agent that 3-chloro-2-hydroxypropyl-trimethyl ammonium chloride or 2,3-epoxypropyltrimethylchloride chloride and natural macromolecular material are synthesized by etherification technology makes some progress.Taking treated starch as example: the patent No. discloses a kind of high degree of substitution quaternary ammonium cationic starch flocculating agent and synthetic method thereof as the patent of invention of 200610166835.X, notification number is the technique that the patent of invention of CN1352196A discloses a kind of preparing quaternary ammonium cation starch by semi-dry method, the substitution value of industrial etherificate type starch used is generally lower than 0.2 at present, although the cationic starch ether performance of high substitution value is good, but more difficult preparation, reaction efficiency is lower, cost is higher, as Thomas Heinze has prepared the cationic starch ether that substitution value is 1.05, reaction efficiency is only 52%, while selecting the mol ratio of cationic starch and etherifying agent to be 1:10 when secondary etherificate, substitution value is up to 1.5, but reaction efficiency is only up to 10%, except preparation technology's factor, the Low-substituted Cationic Starch generating is because of sterically hindered and own positively charged, also having suppressed it occurs further to replace.
Etherification modified main employing dry method and wet method, although wherein dry method is without the three wastes, the advantage such as technique is simple, reaction time is short, reaction conversion ratio is low, high to equipment requirements, unstable product quality, only has minority producer to adopt this method to produce; Wet method is the main method adopting at present, is also the method adopting the earliest, and product, the reaction efficiency that can obtain higher conversion are high, equipment requirements is low, technique is simple, but has the three wastes, rear washing and the equipment cost such as dry is large etc. that problem is difficult to process.
Summary of the invention
In order to overcome the deficiencies in the prior art, the invention provides a kind of high degree of substitution quaternary ammonium type polysaccharide bioflocculant and preparation method thereof, this flocculation agent is taking non-ionic type polysaccharide bioflocculant as raw material, this raw material is large-scale production and leading in the world, nontoxic, environment-friendly biodegradable, the present invention adopts wet processing, workable, technique is simple, reaction conditions gentleness, reaction conversion ratio is high, easily washing separates, consuming time short, waste liquid is also recycled, the product making is buff powder, nontoxic, solubility is strong, cheap, can be used for drinking water treatment, different sewage is had more to obvious flocculating effect simultaneously, there is significant environmental and social benefits.
The technical solution adopted for the present invention to solve the technical problems is: a kind of high degree of substitution quaternary ammonium type polysaccharide bioflocculant, and taking non-ionic type polysaccharide bioflocculant solution as raw material, a kind of quaternary ammonium type polysaccharide bioflocculant making, its molecular structure skeleton symbol is: wherein Dx is non-ionic type polysaccharide bioflocculant, and its skeleton symbol is:
wherein n=10,000-310,000.Its position of substitution mainly occurs on C2, C3 or C4 position.
The preparation method of the raw material non-ionic type polysaccharide bioflocculant that the present invention adopts is the activator that adds Sucrose:glucan alpha1-6-glucosyltransferase in certain density sucrose solution, then regulate the pH value of this solution, after add Sucrose:glucan alpha1-6-glucosyltransferase solution, again regulate constant temperature stirring reaction for some time after pH, obtain the sterilizing of reaction product post-heating, filtration, removal of impurities, purifying and obtain the finished product after concentrated, it is a kind of Enzymology method of preparing polysaccharide bioflocculant described in CN101392280A that concrete preparation method is preferably patent announcement number, and its concrete preparation method is as follows:
The preferred kinetic viscosity of described non-ionic type polysaccharide bioflocculant is respectively 4500cPs, 11250cPs, 40100cPs and 65000cPs, comprises following making step:
(1), according to the requirement of above-mentioned polysaccharide bioflocculant kinetic viscosity, compound concentration is 1000 milliliters, 5000 milliliters, 100 liters and 1000 liters of the sucrose solutions of 0.80mol/L, 0.73mol/L, 0.58mol/L and 0.44mol/L accordingly respectively;
(2) in above-mentioned sucrose solution, add respectively calcium chloride solution, wherein concentration is in the solution of 0.80mol/L and 0.73mol/L, to add respectively 10 milliliters and 50 milliliters of 0.5% calcium chloride solutions; Concentration is in the solution of 0.58mol/L and 0.44mol/L, to add respectively 100 milliliters and 1000 milliliters of 5% calcium chloride solutions;
(3) regulate the pH value of above-mentioned sucrose solution in 5.2~5.4 scopes with 30% hac buffer;
(4) to adding respectively 17.5 milliliters of Sucrose:glucan alpha1-6-glucosyltransferase solution, 109.6 milliliters, 2500 milliliters and 29.2 liters in above-mentioned sucrose solution, the activity of enzyme is respectively 456IU/ml, 456IU/ml, 480IU/ml and 480IU/ml, after mixing, with 10% vinegar acid for adjusting pH value in 5.2~5.4 scopes;
(5) above-mentioned solution is placed in to water bath with thermostatic control, regulate and stir, fully reaction is until solution reaches desired kinetic viscosity, and the water bath with thermostatic control temperature corresponding to solution of above-mentioned 0.80mol/L, 0.73mol/L, 0.58mol/L and tetra-kinds of different concns of 0.44mol/L is respectively 20~22 DEG C, 22~24 DEG C, 24~26 DEG C, 24~26 DEG C;
(6) reaction product is carried out to heat sterilization, filtering and impurity removing, obtains described non-ionic type polysaccharide bioflocculant after purifying is concentrated.
A kind of preparation method of described high degree of substitution quaternary ammonium type polysaccharide bioflocculant, it is characterized in that: adopt wet processing, by adding catalyzer and promotor to carry out alkalinisation treatment in the non-ionic type polysaccharide bioflocculant solution that is 4~40% to mass concentration, a certain amount of dispersion agent of rear slowly dropping, stir, finally add etherifying agent reaction for some time, through precipitation, washing, alcohol wash, dry, grind and make the finished product.
Wherein, non-ionic type polysaccharide bioflocculant is 1:0.2~1:6 with the solid masses ratio of etherifying agent, the mass ratio of catalyzer and promotor is 1:0.1~1:3, the mol ratio of catalyzer and etherifying agent is 1:2~1:10, dispersion agent volume used accounts for 5~20% of water volume in reaction system, and the temperature of alkalization and etherification reaction is all 20~40 DEG C, and alkalization time is 10~60min, after dispersion agent adds, stir 0.5~1h, the etherificate time is 1~3h.
Described catalyzer is any one in sodium hydroxide, potassium hydroxide, sodium oxide, potassium oxide, sodium carbonate, sodium bicarbonate.
Described promotor is any one in urea, Monoethanolamine MEA BASF, diethanolamine, trolamine, monoisopropanolamine, diisopropanolamine (DIPA), tri-isopropanolamine, diglycolamine.
Described etherifying agent is 3-chloro-2-hydroxypropyl-trimethyl ammonium chloride (CTA), any one in 2,3-epoxypropyltrimethylchloride chloride (GTA).
Described dispersion agent is any one in methyl alcohol, ethanol, Virahol, acetone, ether.
The substitution value of described high degree of substitution quaternary ammonium type polysaccharide bioflocculant is 0.2-1.8, molecular weight 2,000,000-50,000,000.
Its reaction principle is as follows:
Remarkable advantage of the present invention is:
1. product appearance of the present invention is pale yellow powder, product is nontoxic, environmental protection, efficient, belong to the modified product of polysaccharide bioflocculant, at present the Biodegradable material such as such as modified starch series, modified-cellulose class of preparation all adopts dry method or semidrying preparation technology because of labile factors such as the facile hydrolysiss of etherifying agent, the product that the present invention adopts wet processing to prepare, not only good stability and simple to operate, easily separated, high without the three wastes, cost performance.
2. product of the present invention all has obvious flocculating effect to tap water and dyeing waste water, coal washing water, ore dressing, refinery water, papermaking and wastewater from chemical industry etc., and the problems that solved that metal residual, sludge quantity that the conventional in the market inorganic salt such as poly-aluminium, Polyferric Sulfate bring are large, corrosion pipeline and the monomer residue of polyacrylamide in water body etc. exist, its performance can compare favourably with it, and this series products has market outlook and good economic results in society widely.
3. product of the present invention carries out non-ionic type polysaccharide bioflocculant leading in the world quaternised modified, makes it have ultra-high molecular weight and high charge density, and this series products there is not yet report.
Embodiment
Below to a preferred embodiment of the present invention will be described in detail.
Embodiment 1
1. quaternization: get mass concentration and be 4% nonionic biological flocculant aqueous solution 200g in 500ml there-necked flask, start stirring, then add sodium carbonate solid 4.5g to add 9g urea after 30 DEG C of stirred in water bath are dissolved, continue to stir 10min.
2. etherification reaction: slowly stir 0.5h after the Virahol of dropping 20ml in 30 DEG C of water-baths in reaction system, be then evenly sprinkled into 16g2 in reaction system, 3-epoxypropyltrimethylchloride chloride (GTA), continues stirring reaction 2h.
3. product processing: take out reaction product, after precipitation with filter paper filtering, then washing, alcohol wash, dry, grind, make light yellow substitution value and be 1.60 quaternary ammonium type polysaccharide bioflocculant.
Embodiment 2
1. quaternization: get mass concentration and be 15% nonionic biological flocculant aqueous solution 200g in 500ml there-necked flask, start stirring, then add sodium oxide solid 8g, after 25 DEG C of stirred in water bath are dissolved, add 4g diglycolamine, continue stirring reaction 30min.
2. etherification reaction: slowly drip 3-chloro-2-hydroxypropyl-trimethyl ammonium chloride (CTA) aqueous solution that 50g mass concentration is 60% in reaction system, then continue stirring reaction 2h.
3. product processing: the light yellow fluid that product is thickness, admittedly be 31% containing thing content, through washing, alcohol wash and dry and grind that to make light yellow substitution value be 0.23 quaternary ammonium type polysaccharide bioflocculant.
Embodiment 3
1. quaternization: get mass concentration and be 16.7% nonionic biological flocculant aqueous solution 200g in 500ml there-necked flask, start stirring, then add sodium hydrate solid 2.8g, after 30 DEG C of stirred in water bath are dissolved, add 2.8g trolamine, continue stirring reaction 10min.
2. etherification reaction: to the acetone that slowly adds 30ml in reaction system, after add 53.44g2,3-epoxypropyltrimethylchloride chloride (GTA), then continues stirring reaction 1.5h.
3. product processing: the brown color paste that product is thickness, admittedly be 35% containing thing content, through washing, alcohol wash and dry and grind that to make light yellow substitution value be 2.41 quaternary ammonium type polysaccharide bioflocculant.
Embodiment 4
1. quaternization: get mass concentration and be 15.3% nonionic biological flocculant aqueous solution 200g in 500ml there-necked flask, start stirring, then add sodium bicarbonate solid 8g, after 25 DEG C of stirred in water bath are dissolved, add 8g tri-isopropanolamine, rear continuation stirring reaction 60min.
2. etherification reaction: stir 20min to slowly dripping methyl alcohol 28.5ml in reaction system, then slowly adding 51g concentration is 60% 3-chloro-2-hydroxypropyl-trimethyl ammonium chloride (CTA) aqueous solution, continues stirring reaction 3h.
3. product processing: the light yellow fluid that product is thickness, admittedly be 29.1% containing thing content, after precipitation with filter paper filtering, then washing, alcohol wash and dry grinding to make light yellow substitution value be 0.18 quaternary ammonium type polysaccharide bioflocculant.
Above-described is only the preferred embodiments of the present invention; institute is understood that; the explanation of above embodiment is just for helping to understand method of the present invention and core concept thereof; the protection domain being not intended to limit the present invention; all any amendments of making, be equal to replacement etc., within protection scope of the present invention all should be included within thought of the present invention and principle.

Claims (6)

1. a high degree of substitution quaternary ammonium type polysaccharide bioflocculant, is characterized in that: taking non-ionic type polysaccharide bioflocculant solution as raw material, the molecular structure skeleton symbol of the quaternary ammonium type polysaccharide bioflocculant making is: wherein Dx is non-ionic type polysaccharide bioflocculant, and its skeleton symbol is:
wherein n=10,000-310,000.
2. the preparation method of a high degree of substitution quaternary ammonium type polysaccharide bioflocculant as claimed in claim 1, it is characterized in that: adopt wet processing, by adding catalyzer and promotor to carry out alkalinisation treatment in the non-ionic type biofloculation agent solution that is 4~40% to mass concentration, a certain amount of dispersion agent of rear slowly dropping, stir, finally add etherifying agent reaction for some time, through precipitation, washing, alcohol wash, dry, grind and make the finished product; Wherein non-ionic type polysaccharide bioflocculant is 1:0.2~1:6 with the solid masses ratio of etherifying agent, the mass ratio of catalyzer and promotor is 1:0.1~1:3, the mol ratio of catalyzer and etherifying agent is 1:2~1:10, dispersion agent volume used accounts for 5~20% of water volume in reaction system, the temperature of alkalization and etherification reaction is all 20~40 DEG C, alkalization time is 10~60min, after dispersion agent adds, stirs 0.5~1h, and the etherificate time is 1~3h.
3. the preparation method of a kind of high degree of substitution quaternary ammonium type polysaccharide bioflocculant according to claim 2, is characterized in that: described catalyzer is any one in sodium hydroxide, potassium hydroxide, sodium oxide, potassium oxide, sodium carbonate, sodium bicarbonate.
4. the preparation method of a kind of high degree of substitution quaternary ammonium type polysaccharide bioflocculant according to claim 2, is characterized in that: described promotor is any one in urea, Monoethanolamine MEA BASF, diethanolamine, trolamine, monoisopropanolamine, diisopropanolamine (DIPA), tri-isopropanolamine, diglycolamine.
5. the preparation method of a kind of high degree of substitution quaternary ammonium type polysaccharide bioflocculant according to claim 2, it is characterized in that: described etherifying agent is 3-chloro-2-hydroxypropyl-trimethyl ammonium chloride (CTA), any one in 2,3-epoxypropyltrimethylchloride chloride (GTA).
Described dispersion agent is any one in methyl alcohol, ethanol, Virahol, acetone, ether.
6. the preparation method of a kind of high degree of substitution quaternary ammonium type polysaccharide bioflocculant according to claim 2, is characterized in that: the substitution value of described high degree of substitution quaternary ammonium type polysaccharide bioflocculant is 0.2-1.8, molecular weight 2,000,000-50,000,000.
CN201410352573.0A 2014-07-23 2014-07-23 High-substituted quaternary ammonium polysaccharide bioflocculant and preparation method thereof Active CN104130335B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410352573.0A CN104130335B (en) 2014-07-23 2014-07-23 High-substituted quaternary ammonium polysaccharide bioflocculant and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410352573.0A CN104130335B (en) 2014-07-23 2014-07-23 High-substituted quaternary ammonium polysaccharide bioflocculant and preparation method thereof

Publications (2)

Publication Number Publication Date
CN104130335A true CN104130335A (en) 2014-11-05
CN104130335B CN104130335B (en) 2017-04-19

Family

ID=51803224

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410352573.0A Active CN104130335B (en) 2014-07-23 2014-07-23 High-substituted quaternary ammonium polysaccharide bioflocculant and preparation method thereof

Country Status (1)

Country Link
CN (1) CN104130335B (en)

Cited By (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104587974A (en) * 2015-01-23 2015-05-06 江西师范大学 High-cationic-degree cotton fiber and preparation method thereof
CN105217765A (en) * 2015-09-24 2016-01-06 福州大学 A kind of composite macromolecular flocculant and preparation method thereof
CN105417851A (en) * 2015-11-19 2016-03-23 威海汉邦生物环保科技有限公司 Printing and dyeing wastewater treatment method and preparation method of compound biological flocculant
CN106632717A (en) * 2016-12-27 2017-05-10 郭宏昌 Laminarin cationic derivative as well as preparation method and application thereof
CN112998124A (en) * 2021-04-26 2021-06-22 浙江丰宇海洋生物制品有限公司 Preparation method of squid liver paste
US11058111B2 (en) 2018-08-29 2021-07-13 Ecolab Usa Inc. Use of multiple charged cationic compounds derived from primary amines or polyamines for microbial fouling control in a water system
US11084974B2 (en) 2018-08-29 2021-08-10 Championx Usa Inc. Use of multiple charged cationic compounds derived from polyamines for clay stabilization in oil and gas operations
US11155480B2 (en) 2019-01-29 2021-10-26 Ecolab Usa Inc. Use of cationic sugar-based compounds as corrosion inhibitors in a water system
US11155481B2 (en) 2019-01-29 2021-10-26 Ecolab Usa Inc. Use of cationic sugar-based compounds for microbial fouling control in a water system
US11236040B2 (en) 2018-08-29 2022-02-01 Ecolab Usa Inc. Multiple charged ionic compounds derived from polyamines and compositions thereof and methods of preparation thereof
US11261113B2 (en) 2017-08-30 2022-03-01 Ecolab Usa Inc. Molecules having one hydrophobic group and two identical hydrophilic ionic groups and compositions thereof and methods of preparation thereof
US11292734B2 (en) 2018-08-29 2022-04-05 Ecolab Usa Inc. Use of multiple charged ionic compounds derived from poly amines for waste water clarification
US11359291B2 (en) 2019-04-16 2022-06-14 Ecolab Usa Inc. Use of multiple charged cationic compounds derived from polyamines and compositions thereof for corrosion inhibition in a water system
CN114890525A (en) * 2022-05-19 2022-08-12 合肥工业大学 Preparation method and application of dextran-betaine cationic flocculant
US11685709B2 (en) 2018-08-29 2023-06-27 Ecolab Usa Inc. Multiple charged ionic compounds derived from polyamines and compositions thereof and use thereof as reverse emulsion breakers in oil and gas operations

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1990392A (en) * 2005-12-07 2007-07-04 中国科学院成都有机化学有限公司 High degree of substitution quaternary ammonium cationic starch flocculating agent and method for synthesizing same
CN101168569A (en) * 2007-12-04 2008-04-30 天津科技大学 Method for preparing cationic starch with high substitution degree

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1990392A (en) * 2005-12-07 2007-07-04 中国科学院成都有机化学有限公司 High degree of substitution quaternary ammonium cationic starch flocculating agent and method for synthesizing same
CN101168569A (en) * 2007-12-04 2008-04-30 天津科技大学 Method for preparing cationic starch with high substitution degree

Cited By (19)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104587974A (en) * 2015-01-23 2015-05-06 江西师范大学 High-cationic-degree cotton fiber and preparation method thereof
CN105217765A (en) * 2015-09-24 2016-01-06 福州大学 A kind of composite macromolecular flocculant and preparation method thereof
CN105417851A (en) * 2015-11-19 2016-03-23 威海汉邦生物环保科技有限公司 Printing and dyeing wastewater treatment method and preparation method of compound biological flocculant
CN106632717A (en) * 2016-12-27 2017-05-10 郭宏昌 Laminarin cationic derivative as well as preparation method and application thereof
US11261113B2 (en) 2017-08-30 2022-03-01 Ecolab Usa Inc. Molecules having one hydrophobic group and two identical hydrophilic ionic groups and compositions thereof and methods of preparation thereof
US11084974B2 (en) 2018-08-29 2021-08-10 Championx Usa Inc. Use of multiple charged cationic compounds derived from polyamines for clay stabilization in oil and gas operations
US11685709B2 (en) 2018-08-29 2023-06-27 Ecolab Usa Inc. Multiple charged ionic compounds derived from polyamines and compositions thereof and use thereof as reverse emulsion breakers in oil and gas operations
US11236040B2 (en) 2018-08-29 2022-02-01 Ecolab Usa Inc. Multiple charged ionic compounds derived from polyamines and compositions thereof and methods of preparation thereof
US11058111B2 (en) 2018-08-29 2021-07-13 Ecolab Usa Inc. Use of multiple charged cationic compounds derived from primary amines or polyamines for microbial fouling control in a water system
US11292734B2 (en) 2018-08-29 2022-04-05 Ecolab Usa Inc. Use of multiple charged ionic compounds derived from poly amines for waste water clarification
US11926543B2 (en) 2018-08-29 2024-03-12 Ecolab Usa Inc. Use of multiple charged ionic compounds derived from polyamines for waste water clarification
US11702586B2 (en) 2018-08-29 2023-07-18 Championx Usa Inc. Use of multiple charged cationic compounds derived from polyamines for clay stabilization in oil and gas operations
US11155480B2 (en) 2019-01-29 2021-10-26 Ecolab Usa Inc. Use of cationic sugar-based compounds as corrosion inhibitors in a water system
US11155481B2 (en) 2019-01-29 2021-10-26 Ecolab Usa Inc. Use of cationic sugar-based compounds for microbial fouling control in a water system
US11359291B2 (en) 2019-04-16 2022-06-14 Ecolab Usa Inc. Use of multiple charged cationic compounds derived from polyamines and compositions thereof for corrosion inhibition in a water system
US11639553B2 (en) 2019-04-16 2023-05-02 Ecolab Usa Inc. Compositions comprising multiple charged cationic compounds derived from polyamines for corrosion inhibition in a water system
CN112998124A (en) * 2021-04-26 2021-06-22 浙江丰宇海洋生物制品有限公司 Preparation method of squid liver paste
CN114890525A (en) * 2022-05-19 2022-08-12 合肥工业大学 Preparation method and application of dextran-betaine cationic flocculant
CN114890525B (en) * 2022-05-19 2024-01-23 合肥工业大学 Preparation method and application of dextran-betaine cationic flocculant

Also Published As

Publication number Publication date
CN104130335B (en) 2017-04-19

Similar Documents

Publication Publication Date Title
CN104130335A (en) High-substituted quaternary ammonium polysaccharide bioflocculant and preparation method thereof
CN103864266B (en) A kind of waste paper making wastewater, sludge circulation reuse method
CN204824453U (en) Desulfurization pretreatment of water device that gives up
CN104724809B (en) A kind of ternary polymerization flocculant based on natural polymer and preparation method thereof
CN103387321A (en) Processing method capable of recycling iron-containing sludge generated in advanced oxidation techniques
CN102689999A (en) Resourceful treatment method for silica gel waste water
CN102532418B (en) Grating-modified composite bio-flocculant and preparing method thereof
CN101948192A (en) Membrane technology-based papermaking black liquor high-efficiency comprehensive treatment method
CN102702367A (en) Method for preparing cationic cross-linked starch xanthate
CN104017136A (en) Preparation method of amphoteric grafting-type modified cellulose flocculant
CN102642900B (en) Method for preparing inorganic-organic composite flocculant made of polymeric aluminum and modified compound biological flocculant
CN103991982B (en) Method for performing coagulation treatment on waste paper pulping comprehensive papermaking wastewater by utilizing cellulose-based flocculating agent
CN201971688U (en) System for removing silicon and oil of oily sewage
CN105153369A (en) Amphoteric polysaccharide biological flocculant and preparation method thereof
CN103922505A (en) Method for deep treatment on tea bag filter paper making bleach by using nanofiltration membrane
CN104974454A (en) Flocculant and preparation method of same
CN110950521A (en) Chemical treatment method for improving red mud settling separation effect
CN103771611B (en) The solid-liquid separating method of cellulose alcoholic fermentation waste liquid
CN102690516B (en) Biodegradable cross-linked chitosan chelating resin and preparation method thereof
CN102674519A (en) Preparation method of flocculant for sewage treatment
CN202610045U (en) Processing system of heavy-metal-contained acid wastewater
CN213569979U (en) Domestic waste burns flying dust washing waste water decalcification pretreatment system
CN103693725B (en) Treatment method for reducing COD (Chemical Oxygen Demand) in drilling wastewater and well completion wastewater
CN102219290A (en) Complex coagulant for advanced treatment of biochemical tail water, and its preparation method and application
CN102826709A (en) Technique for removing high-concentration sulfate ions in long-chain dibasic acid fermentation waste liquid

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
CP03 Change of name, title or address

Address after: 264200 No. 71 Jiashan Road, Chucun Town, High-tech District, Weihai City, Shandong Province

Patentee after: Weihai Hanbang biological environmental protection Polytron Technologies Inc

Address before: 264209 No. 71 Jiashan Road, Chucun Town, High-tech District, Weihai City, Shandong Province

Patentee before: WEIHAI HANBANG BIOLOGICAL ENVIRONMENTAL PROTECTION SCIENCE & TECHNOLOGY CO., LTD.

CP03 Change of name, title or address
PE01 Entry into force of the registration of the contract for pledge of patent right
PE01 Entry into force of the registration of the contract for pledge of patent right

Denomination of invention: A quaternary ammonium polysaccharide bioflocculant with high degree of substitution and its preparation method

Effective date of registration: 20210525

Granted publication date: 20170419

Pledgee: Weihai City Commercial Bank Limited by Share Ltd. high tech branch

Pledgor: Weihai Hanbang biological environmental protection Polytron Technologies Inc.

Registration number: Y2021980003946

PC01 Cancellation of the registration of the contract for pledge of patent right
PC01 Cancellation of the registration of the contract for pledge of patent right

Date of cancellation: 20220513

Granted publication date: 20170419

Pledgee: Weihai City Commercial Bank Limited by Share Ltd. high tech branch

Pledgor: Weihai Hanbang biological environmental protection Polytron Technologies Inc.

Registration number: Y2021980003946

PE01 Entry into force of the registration of the contract for pledge of patent right
PE01 Entry into force of the registration of the contract for pledge of patent right

Denomination of invention: The invention relates to a quaternary ammonium polysaccharide bioflocculant with high degree of substitution and a preparation method thereof

Effective date of registration: 20220516

Granted publication date: 20170419

Pledgee: Weihai City Commercial Bank Limited by Share Ltd. high tech branch

Pledgor: Weihai Hanbang biological environmental protection Polytron Technologies Inc.

Registration number: Y2022980005577