CN113636632A - Composite polymeric flocculant and preparation method thereof - Google Patents

Composite polymeric flocculant and preparation method thereof Download PDF

Info

Publication number
CN113636632A
CN113636632A CN202111070775.2A CN202111070775A CN113636632A CN 113636632 A CN113636632 A CN 113636632A CN 202111070775 A CN202111070775 A CN 202111070775A CN 113636632 A CN113636632 A CN 113636632A
Authority
CN
China
Prior art keywords
parts
flocculant
finished product
preparing
water
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
CN202111070775.2A
Other languages
Chinese (zh)
Inventor
彭益云
杜翠翠
李慧晓
毕学敏
李峰
刘世沛
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.)
Henan Yiqun Environmental Protection Technology Co ltd
Original Assignee
Henan Yiqun Environmental Protection 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 Henan Yiqun Environmental Protection Technology Co ltd filed Critical Henan Yiqun Environmental Protection Technology Co ltd
Priority to CN202111070775.2A priority Critical patent/CN113636632A/en
Publication of CN113636632A publication Critical patent/CN113636632A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
    • C02F1/56Macromolecular compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08FMACROMOLECULAR COMPOUNDS OBTAINED BY REACTIONS ONLY INVOLVING CARBON-TO-CARBON UNSATURATED BONDS
    • C08F220/00Copolymers of compounds having one or more unsaturated aliphatic radicals, each having only one carbon-to-carbon double bond, and only one being terminated by only one carboxyl radical or a salt, anhydride ester, amide, imide or nitrile thereof
    • C08F220/02Monocarboxylic acids having less than ten carbon atoms; Derivatives thereof
    • C08F220/04Acids; Metal salts or ammonium salts thereof
    • C08F220/06Acrylic acid; Methacrylic acid; Metal salts or ammonium salts thereof

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Water Supply & Treatment (AREA)
  • Medicinal Chemistry (AREA)
  • Polymers & Plastics (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Health & Medical Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

The invention provides a composite polymeric flocculant and a preparation method thereof, belonging to the technical field of flocculants, wherein the composite polymeric flocculant comprises the following raw materials in parts by weight: 50-200 parts of acrylamide, 40-190 parts of acrylic acid, 15-80 parts of sodium hydroxide, 0.2-4 parts of potassium persulfate, 0.1-3 parts of sodium thiosulfate, 0.01-0.5 part of ascorbic acid, 0.05-50 parts of isopropanol, 0.2-1 part of sulfuric acid, 200-1000 parts of ferrous sulfate, 0.001-0.01 part of sodium nitrite and 300-1500 parts of water; the composite flocculant is adopted, and after the organic flocculant and the inorganic flocculant are mixed, the organic flocculant plays a role of bridging, and floccules generated by the inorganic flocculant are connected together to form larger floccules, so that the sedimentation of the microparticles is accelerated, the wastewater treatment effect is effectively improved by adopting the composite flocculant, and the wastewater treatment cost is reduced.

Description

Composite polymeric flocculant and preparation method thereof
Technical Field
The invention relates to the technical field of flocculating agents, in particular to a composite polymeric flocculating agent and a preparation method thereof.
Background
The theoretical basis of the flocculant is as follows: the 'coalescence' theory, the flocculating agent is mainly that some particles or granules which have positive (negative) electric property and are difficult to separate and have negative (positive) electric property in water are close to each other, the electric potential of the flocculating agent is reduced, the flocculating agent is in an unstable state, the particles are concentrated by utilizing the polymerization property of the flocculating agent and are separated by a physical or chemical method, and the flocculating agent is mainly applied to the field of sewage treatment.
During the mining or production operation of metallurgical mine, can dissolve out the ore pulp, because the ore pulp contains most harmful substance such as all contain heavy metal, consequently, need handle earlier when the discharge, the characteristics of mine waste water or ore pulp are: the waste water amount is large, and the water flow time is long; the water discharging points are dispersed, the water quality and the water quantity change greatly along with seasons and climates, and the water discharging device is rich in various metal ions and the like.
The main method for treating mine ore pulp or wastewater at present is a coagulating sedimentation method, wherein the coagulating sedimentation method is adsorption sedimentation by using a flocculating agent, and the coagulating sedimentation method is the most effective and simplest method.
Disclosure of Invention
In view of the above, the present invention provides a composite polymeric flocculant and a preparation method thereof, so as to solve the following problems existing in the existing traditional manufacturing process: the mine ore pulp waste water amount is large, the water flow time is long, various substances are complex and different, and a single flocculating agent is difficult to treat.
In order to solve the technical problems, the invention provides a composite polymeric flocculant, which comprises the following raw materials in parts by weight: 50-200 parts of acrylamide, 40-190 parts of acrylic acid, 15-80 parts of sodium hydroxide, 0.2-4 parts of potassium persulfate, 0.1-3 parts of sodium thiosulfate, 0.01-0.5 part of ascorbic acid, 0.05-50 parts of isopropanol, 0.2-1 part of sulfuric acid, 200-1000 parts of ferrous sulfate, 0.001-0.01 part of sodium nitrite and 300-1500 parts of water.
The preparation method of the composite polymeric flocculant is characterized by comprising the following steps:
(1) preparing an organic flocculant, dissolving sodium hydroxide in water, neutralizing with acrylic acid in a reaction kettle, adding acrylamide after neutralization, dissolving sodium thiosulfate, ascorbic acid and isopropanol in water, adding the sodium thiosulfate, the ascorbic acid and the isopropanol into the reaction kettle, finally dissolving potassium persulfate in water, adding the potassium persulfate into the reaction kettle, initiating a polymerization reaction at the temperature of 15-45 ℃, carrying out adiabatic natural heating, wherein the polymerization reaction time is 20-80 min, and granulating, drying and crushing after the reaction is finished to obtain polyacrylamide powder;
(2) preparing an inorganic flocculant, namely sequentially adding sulfuric acid, ferrous sulfate and water into a reaction tank, then connecting the solution into a reaction kettle, adding oxygen and sodium nitrite, discharging a finished product solution into a finished product tank after the ferrous ions in the solution are reacted, introducing a liquid finished product into a spray tower through a pipeline in the finished product tank, spraying the liquid finished product out of a high-pressure spray head, blowing high-temperature hot air heated by a hot blast stove into the tower, and quickly drying atomized polymeric ferric sulfate in the air to produce a solid finished product, wherein the sprayed solid finished product is discharged from a material receiving port;
(3) and stirring and mixing the prepared polyacrylamide powder and polymeric ferric sulfate, and bagging.
Further, the ratio of the polyacrylamide powder to the polymeric ferric sulfate is 1: 3 to 4.
Further, the dosage ratio of the sodium hydroxide to the acrylic acid is 2: 5.
further, the reaction temperature for preparing the polyacrylamide is 20-45 ℃.
Further, the time of the polymerization reaction is 60-70 min.
Furthermore, the amount of the sodium nitrite is 1-2 g per ton of finished products. .
Compared with the prior art, the invention has the beneficial technical effects that:
1. the composite flocculant is adopted, and after the organic flocculant and the inorganic flocculant are mixed, the organic flocculant plays a role of bridging, and floccules generated by the inorganic flocculant are connected together to form larger floccules, so that the sedimentation of the microparticles is accelerated, the wastewater treatment effect is effectively improved by adopting the composite flocculant, and the wastewater treatment cost is reduced.
Detailed Description
The following examples are given to illustrate specific embodiments of the present invention, but are not intended to limit the scope of the present invention in any way. The instruments and devices referred to in the following examples are conventional instruments and devices unless otherwise specified; the industrial raw materials are all conventional industrial raw materials which are sold on the market if not specifically indicated; the processing and manufacturing methods are conventional methods unless otherwise specified.
Example 1:
a composite polymeric flocculant comprises the following raw materials in parts by weight: 90 parts of acrylamide, 120 parts of acrylic acid, 50 parts of sodium hydroxide, 0.4 part of potassium persulfate, 0.5 part of sodium thiosulfate, 0.02 part of ascorbic acid, 3 parts of isopropanol, 0.8 part of sulfuric acid, 800 parts of ferrous sulfate, 0.008 part of sodium nitrite and 1200 parts of water.
The preparation method of the composite polymeric flocculant is characterized by comprising the following steps:
(1) preparing an organic flocculant, namely dissolving 50 parts of sodium hydroxide in 350 parts of water, neutralizing with 120 parts of acrylic acid in a reaction kettle, adding 90 parts of acrylamide after neutralization, dissolving 0.5 part of sodium thiosulfate, 0.02 part of ascorbic acid and 3 parts of isopropanol in 40 parts of water, adding 0.4 part of potassium persulfate in 10 parts of water into the reaction kettle, initiating a polymerization reaction at the temperature of 20 ℃, carrying out adiabatic natural temperature rise, wherein the polymerization reaction time is 60min, and granulating, drying and crushing after the reaction is finished to obtain polyacrylamide powder;
(2) preparing an inorganic flocculant, namely sequentially adding 0.8 part of sulfuric acid, 800 parts of ferrous sulfate and 800 parts of water into a reaction tank, then connecting the solution and adding into a reaction kettle, adding oxygen and 0.008 part of sodium nitrite, discharging the finished solution into a finished product tank after the reaction of ferrous ions in the solution is finished, introducing the liquid finished product into a spray tower through a pipeline in the finished product tank, spraying out the liquid finished product through a high-pressure spray head, blowing high-temperature hot air heated by a hot blast stove into the tower, and quickly drying atomized polymeric ferric sulfate in the air to produce a solid finished product, wherein the sprayed solid finished product is discharged from a material receiving port;
(3) and stirring and mixing the prepared polyacrylamide powder and polymeric ferric sulfate, and bagging.
In this example, the concentration of the prepared polyacrylamide gel is relatively low, and the drying time is long.
Example 2:
a composite polymeric flocculant comprises the following raw materials in parts by weight: 125 parts of acrylamide, 185 parts of acrylic acid, 75 parts of sodium hydroxide, 0.5 part of potassium persulfate, 0.25 part of sodium thiosulfate, 0.05 part of ascorbic acid, 40 parts of isopropanol, 0.9 part of sulfuric acid, 900 parts of ferrous sulfate, 0.009 part of sodium nitrite and 1100 parts of water.
The preparation method of the composite polymeric flocculant is characterized by comprising the following steps:
(1) preparing an organic flocculant, namely dissolving 75 parts of sodium hydroxide in 160 parts of water, neutralizing with 185 parts of acrylic acid in a reaction kettle, adding 125 parts of acrylamide after neutralization, dissolving 0.25 part of sodium thiosulfate, 0.05 part of ascorbic acid and 40 parts of isopropanol in 30 parts of water, adding 0.5 part of potassium persulfate in 10 parts of water into the reaction kettle, initiating a polymerization reaction at the temperature of 30 ℃, raising the temperature naturally in an adiabatic manner, wherein the polymerization reaction time is 70min, and granulating, drying and crushing after the reaction is finished to obtain polyacrylamide powder;
(2) preparing an inorganic flocculant, namely sequentially adding 0.9 part of sulfuric acid, 900 parts of ferrous sulfate and 900 parts of water into a reaction tank, then connecting the solution and adding into a reaction kettle, adding oxygen and 0.009 part of sodium nitrite, discharging the finished solution into a finished product tank after the reaction of ferrous ions in the solution is finished, introducing the liquid finished product into a spray tower through a pipeline in the finished product tank, spraying out the liquid finished product through a high-pressure spray head, blowing high-temperature hot air heated by a hot blast stove into the tower, and quickly drying atomized polyferric sulfate in the air to produce a solid finished product, wherein the sprayed solid finished product is discharged from a material receiving port;
(3) and stirring and mixing the prepared polyacrylamide powder and polymeric ferric sulfate, and bagging.
In this embodiment, the prepared polyacrylamide gel has a high concentration and a high drying speed, and the ratio of the polyacrylamide powder to the polyferric sulfate is 1: 3, the effect is good in use.
While the present invention has been described in detail with reference to the embodiments, those skilled in the art will appreciate that various changes and modifications can be made in the specific parameters of the embodiments without departing from the spirit of the present invention, and it is intended to cover all the modifications and changes of the present invention.

Claims (7)

1. The composite polymeric flocculant is characterized by comprising the following raw materials in parts by weight:
50-200 parts of acrylamide, 40-190 parts of acrylic acid, 15-80 parts of sodium hydroxide, 0.2-4 parts of potassium persulfate, 0.1-3 parts of sodium thiosulfate, 0.01-0.5 part of ascorbic acid, 0.05-50 parts of isopropanol, 0.2-1 part of sulfuric acid, 200-1000 parts of ferrous sulfate, 0.001-0.01 part of sodium nitrite and 300-1500 parts of water.
2. The method for preparing a composite polymeric flocculant according to claim 1, comprising the steps of:
(1) preparing an organic flocculant, dissolving sodium hydroxide in water, neutralizing with acrylic acid in a reaction kettle, adding acrylamide after neutralization, dissolving sodium thiosulfate, ascorbic acid and isopropanol in water, adding the sodium thiosulfate, the ascorbic acid and the isopropanol into the reaction kettle, finally dissolving potassium persulfate in water, adding the potassium persulfate into the reaction kettle, initiating a polymerization reaction at the temperature of 15-45 ℃, carrying out adiabatic natural heating, wherein the polymerization reaction time is 20-80 min, and granulating, drying and crushing after the reaction is finished to obtain polyacrylamide powder;
(2) preparing an inorganic flocculant, namely sequentially adding sulfuric acid, ferrous sulfate and water into a reaction tank, then connecting the solution into a reaction kettle, adding oxygen and sodium nitrite, discharging a finished product solution into a finished product tank after the ferrous ions in the solution are reacted, introducing a liquid finished product into a spray tower through a pipeline in the finished product tank, spraying the liquid finished product out of a high-pressure spray head, blowing high-temperature hot air heated by a hot blast stove into the tower, and quickly drying atomized polymeric ferric sulfate in the air to produce a solid finished product, wherein the sprayed solid finished product is discharged from a material receiving port;
(3) and stirring and mixing the prepared polyacrylamide powder and polymeric ferric sulfate, and bagging.
3. The method for preparing the composite polymeric flocculant of claim 2, wherein the ratio of the polyacrylamide powder to the polymeric ferric sulfate is 1: 3 to 4.
4. The method according to claim 2, wherein the ratio of the sodium hydroxide to the acrylic acid is 2: 5.
5. the method for preparing the composite polymeric flocculant according to claim 2, wherein the reaction temperature for preparing the polyacrylamide is 20-45 ℃.
6. The method for preparing the composite polymeric flocculant according to claim 2, wherein the polymerization reaction time is 60 to 70 min.
7. The method for preparing the composite polymeric flocculant according to claim 2, wherein the amount of the sodium nitrite is 1 to 2g per ton of finished product.
CN202111070775.2A 2021-09-13 2021-09-13 Composite polymeric flocculant and preparation method thereof Pending CN113636632A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202111070775.2A CN113636632A (en) 2021-09-13 2021-09-13 Composite polymeric flocculant and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202111070775.2A CN113636632A (en) 2021-09-13 2021-09-13 Composite polymeric flocculant and preparation method thereof

Publications (1)

Publication Number Publication Date
CN113636632A true CN113636632A (en) 2021-11-12

Family

ID=78425680

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202111070775.2A Pending CN113636632A (en) 2021-09-13 2021-09-13 Composite polymeric flocculant and preparation method thereof

Country Status (1)

Country Link
CN (1) CN113636632A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114456300A (en) * 2021-12-30 2022-05-10 云南森博混凝土外加剂有限公司 Flocculant for sand washing and dressing and preparation method thereof

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101831030A (en) * 2010-06-09 2010-09-15 邵赛 Preparation method of anionic polyacrylamide
CN108529729A (en) * 2018-05-19 2018-09-14 原建光 Preparation method of solid composite water purifying agent
CN109928473A (en) * 2019-03-08 2019-06-25 宁夏水投清水源水处理科技有限公司 A kind of composite water purifying efficient flocculant preparation process

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101831030A (en) * 2010-06-09 2010-09-15 邵赛 Preparation method of anionic polyacrylamide
CN108529729A (en) * 2018-05-19 2018-09-14 原建光 Preparation method of solid composite water purifying agent
CN109928473A (en) * 2019-03-08 2019-06-25 宁夏水投清水源水处理科技有限公司 A kind of composite water purifying efficient flocculant preparation process

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114456300A (en) * 2021-12-30 2022-05-10 云南森博混凝土外加剂有限公司 Flocculant for sand washing and dressing and preparation method thereof

Similar Documents

Publication Publication Date Title
CN107597801B (en) A method of barium slag is handled using ardealite innocent
CN104004130B (en) A kind of composite high-molecular sludge dehydrating agent and preparation method thereof
CN103787473A (en) High-stability sewage treating agent and preparation method thereof
CN112125537B (en) Industrial preparation technology of calcium hydroxide
CN113636632A (en) Composite polymeric flocculant and preparation method thereof
CN101891290A (en) Composite purifying agent used for chemical-mechanical pulp advanced waste water treatment and preparation method thereof
CN105084498B (en) A kind of preparation method and application of chitin modified collagen iron and manganese oxides
CN103922453A (en) Flocculating agent for coking wastewater and preparation method thereof and application thereof
CN101851054B (en) Sludge dewatering conditioner, and preparation method and application thereof
CN106335984A (en) Composite water cleaning agent for wastewater ultralow emission treatment and preparation method of composite water cleaning agent
CN106698890A (en) Method for preparing sludge treating agent through waste acid containing ferrous ions
CN104986805A (en) Production method for polyferric chloride sulfate
CN107118820A (en) A kind of coal arsenic removing method and its additive
CN105967484A (en) Sludge deep dehydration method for processing flue gas desulfurization wastewater sludge
CN102173491A (en) Process for comprehensively utilizing rare-earth ore leaching waste liquid and calcining waste heat in rare earth production
CN114853109A (en) Deep defluorination medicament and preparation method and use method thereof
CN106630293A (en) Emergency treatment method for antimony-exceeded waste water at low temperature
CN112723511A (en) High-salt-content desulfurization wastewater treatment flocculant for power plant
CN205803188U (en) A kind of hydrochloric acid lime method processes the device of fluoride waste
CN104496093A (en) Method for performing purification treatment on titanium white wastewater by utilizing salt slurry
CN104817251B (en) A kind of composite high-molecular sludge dehydrating agent and preparation method thereof
CN104355375A (en) Method of utilizing hydrochloric acid pickling liquid waste to prepare compound ferrous flocculant
CN105601771B (en) Microwave radiation technology prepares polyacrylamide glutathione aluminium chloride method and application
CN213012149U (en) Waste water neutralization premixing reaction device and neutralization system
CN108341475A (en) A kind of method and application preparing polysilicon acid titanium flocculant using cold rolling titanium plate pickle liquor

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
RJ01 Rejection of invention patent application after publication

Application publication date: 20211112