CN106630057A - Fly ash composite polyferric sulfate flocculating agent and preparation method thereof - Google Patents
Fly ash composite polyferric sulfate flocculating agent and preparation method thereof Download PDFInfo
- Publication number
- CN106630057A CN106630057A CN201611149585.9A CN201611149585A CN106630057A CN 106630057 A CN106630057 A CN 106630057A CN 201611149585 A CN201611149585 A CN 201611149585A CN 106630057 A CN106630057 A CN 106630057A
- Authority
- CN
- China
- Prior art keywords
- parts
- attapulgite
- flyash
- fly ash
- flocculating agent
- 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
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
- C02F1/5245—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/54—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/54—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
- C02F1/56—Macromolecular compounds
Landscapes
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
The invention discloses a fly ash composite polyferric sulfate flocculating agent and a preparation method thereof. The fly ash composite polyferric sulfate flocculating agent is characterized by being prepared from the following raw materials in parts by weight: 2 to 4 parts of fly ash, 25 to 30 parts of FeS04 7H20, 1 to 2 parts of red soil, a proper amount of sulphuric acid waste liquid, 2 to 3 parts of thiobacillus ferrooxidans, 4 to 6 parts of hydrogen peroxide, 3 to 5 parts of silver nitrate, 1 to 2 parts of iron chloride, 3 to 5 parts of polyacrylamide VN835, 15 to 25 parts of attapulgite, 25 to 35 parts of glycol and 25 to 30 parts of water. The attapulgite is used for loading the polyferric sulfate, so that the acting force between flocculating agent molecules changes, so that an adsorption layer is firmer and compactor; the flocculating performance of the flocculating agent is increased and improved; the flocculating effect is enhanced. The fly ash and the high-molecular flocculating agent are compounded, i.e., the sewage treatment effect of the agent is enhanced; the fly ash is changed from waste materials into valuable materials; the integral utilization is realized.
Description
Technical field
The present invention relates to a kind of flyash composite polymeric ferric sulfate flocculant and its system of the water process such as water supply draining
Preparation Method, belongs to field of environment engineering technology.
Background technology
Bodied ferric sulfate is a kind of new, high-quality, efficient molysite class inorganic polymer flocculant, is mainly used in purifying water effect
Excellent, water quality is good, and without harmful substances such as aluminium, chlorine and heavy metal ion, also the water of non-iron-ion is nontoxic to transfer, harmless, peace
It is complete reliable, turbidity removal, decolouring, de-oiling, dehydration, it is degerming, deodorant, except algae, remove COD, BOD and heavy metal ion in eliminating water the effects such as
Significantly etc..It is also used for Industrial Wastewater Treatment, such as dyeing waste water.
Attapulgite is a kind of aqueous magnalium carbonate clay mineral, and the basic structural unit of attapulgite is parallel to carbon
The silicon-oxy tetrahedron double-strand composition of axle, each interchain is connected by oxygen atom, and the interlayer up and down of each double-strand passes through one layer of magnesium original
The sexavalence coordination connection of son.The sensing (i.e. the angle top of silicon-oxy tetrahedron) of silicon-oxy tetrahedron active oxygen atom is upper and lower per tetrad
It is alternately arranged.Due to there is crystal duct in crystal structure, internal surface area is larger, thus with very strong physical absorption performance.
Road is reached in its Ph.D. Dissertation《Bodied ferric sulfate and ferric sulfate of polymerized silica are prepared and organically-modified research》In, utilize
Oxidizing process is prepared for a kind of bodied ferric sulfate, but its flocculating effect, turbidity removal rate need further raising.
The content of the invention
Thinking based on more than, the present invention is intended to provide a kind of flocculating effect is good, the high composite ferric sulfate polymer of turbidity removal rate
Flocculant and preparation method thereof.
The technical problem to be solved is realized using following technical scheme:
A kind of flyash composite polymeric ferric sulfate flocculant, it is characterised in that be made up of the raw material of following weight portion:
Flyash 2-4, FeS04·7H20 25-30, red soil 1-2, appropriate sulfuric acid waste, Thiobacillus ferrooxidans 2-3, hydrogen peroxide
4-6, silver nitrate 3-5, iron chloride 1-2, polyacrylamide VN835 3-5, attapulgite 15-25, ethylene glycol 25-35, water 25-
30;
The mass fraction of the sulfuric acid waste is not less than 60%.
Described a kind of flyash composite polymeric ferric sulfate flocculant and preparation method thereof, it is characterised in that by following step
Suddenly make:
A. by FeS04·7H20 is soluble in water, adds moderate amount of sulfuric acid waste liquid, and regulation pH is 1-2, adds Thiobacillus ferrooxidans,
Hydrogen peroxide, ventilation culture 2-3 days are dropwise instilled at 18-24 DEG C so as to ferrous oxidising into ferric iron, iron chloride is added, in the moon
The dry place of airing is stood after curing certain hour, and impurity screening obtains liquid polymerization ferric sulfate;
B. attapulgite is bakeed into 40-80min at 300 DEG C -700 DEG C, 1-2h is soaked with sulfuric acid waste after cooling, filtered, water
It is washed till after neutrality and is ground, uses 150-250 mesh sieves, drying for standby;
C. step b gained attapulgite and flyash, red soil are added in ethylene glycol solution, suspension are obtained after ultrasonic disperse,
Silver nitrate, polyacrylamide VN835 are added, after immersion 2-5h, centrifugation, washing is vacuum dried under the conditions of 25-55 DEG C, obtains
Absorption polyacrylamide VN835, and carry attapulgite, flyash, the red soil mixture of silver;
D. step c gained mixture is added in step a gained liquid, 1h-6h is stirred at 30-70 DEG C, filtered, then
In 30 DEG C of -50 DEG C of drying, powdery is ground to form.
A kind of described flyash composite polymeric ferric sulfate flocculant and preparation method thereof, it is characterised in that curing time
It is all for 2-4.
The invention has the beneficial effects as follows:Add Thiobacillus ferrooxidans as biocatalyst in oxidizing process, safely may be used
By, energy-conserving and environment-protective;Bodied ferric sulfate is loaded using attapulgite, the intermolecular forces for causing flocculating agent molecule become
Change, so that adsorption layer is more firmly and tight, increase and improve the flocculating property of flocculant, flocculating effect strengthens;Heating
Attapulgite sulfuric acid waste immersion after activation can remove the impurity being distributed in attapulgite duct, dredge duct, carry
High attapulgite adsorptivity, decolourising property etc..Ethylene glycol can on attapulgite in-situ reducing silver nitrate, make the silver particles of generation
It is attached on attapulgite, gives the function of flocculant antibacterial, increases the service life, meanwhile, polyacrylamide VN835 not only may be used
To cooperate with turbidity removal together with bodied ferric sulfate, load of the silver particles on attapulgite can also be promoted;The present invention is by flyash
With high polymer coagulant compounding, that is, the effect of chemicals treatment sewage is enhanced, make flyash turn waste into wealth again, obtained comprehensive profit
With.
Specific embodiment
With reference to embodiment, the specific embodiment of the present invention is further described.
Embodiment
A kind of flyash composite polymeric ferric sulfate flocculant, it is characterised in that be made up of the raw material of following weight portion:
Flyash 2, FeS04·7H20 30, red soil 2, appropriate sulfuric acid waste, Thiobacillus ferrooxidans 3, hydrogen peroxide 6, silver nitrate
5, iron chloride 2, polyacrylamide VN835 5, attapulgite 25, ethylene glycol 35, water 25;
The mass fraction of the sulfuric acid waste is not less than 60%.
Described a kind of flyash composite polymeric ferric sulfate flocculant and preparation method thereof, it is characterised in that by following step
Suddenly make:
A. by FeS04·7H20 is soluble in water, adds moderate amount of sulfuric acid waste liquid, and regulation pH is 1-2, adds Thiobacillus ferrooxidans,
Hydrogen peroxide, ventilation culture 2-3 days are dropwise instilled at 18-24 DEG C so as to ferrous oxidising into ferric iron, iron chloride is added, in the moon
The dry place of airing is stood after curing certain hour, and impurity screening obtains liquid polymerization ferric sulfate;
B. attapulgite is bakeed into 40-80min at 300 DEG C -700 DEG C, 1-2h is soaked with sulfuric acid waste after cooling, filtered, water
It is washed till after neutrality and is ground, uses 150-250 mesh sieves, drying for standby;
C. step b gained attapulgite and flyash, red soil are added in ethylene glycol solution, suspension are obtained after ultrasonic disperse,
Silver nitrate, polyacrylamide VN835 are added, after immersion 2-5h, centrifugation, washing is vacuum dried under the conditions of 25-55 DEG C, obtains
Absorption polyacrylamide VN835, and carry attapulgite, flyash, the red soil mixture of silver;
D. step c gained mixture is added in step a gained liquid, 1h-6h is stirred at 30-70 DEG C, filtered, then
In 30 DEG C of -50 DEG C of drying, powdery is ground to form.
A kind of described flyash composite polymeric ferric sulfate flocculant and preparation method thereof, it is characterised in that curing time
It is all for 2-4.
The present invention technical parameter be:Remove turbid rate >=95%.
Claims (3)
1. a kind of flyash composite polymeric ferric sulfate flocculant, it is characterised in that be made up of the raw material of following weight portion:
Flyash 2-4, FeS04·7H20 25-30, red soil 1-2, appropriate sulfuric acid waste, Thiobacillus ferrooxidans 2-3, hydrogen peroxide
4-6, silver nitrate 3-5, iron chloride 1-2, polyacrylamide VN835 3-5, attapulgite 15-25, ethylene glycol 25-35, water 25-
30;
The mass fraction of the sulfuric acid waste is not less than 60%.
2. a kind of flyash composite polymeric ferric sulfate flocculant according to claim 1 and preparation method thereof, its feature exists
In being made up of following steps:
A. by FeS04·7H20 is soluble in water, adds moderate amount of sulfuric acid waste liquid, and regulation pH is 1-2, adds Thiobacillus ferrooxidans,
Hydrogen peroxide, ventilation culture 2-3 days are dropwise instilled at 18-24 DEG C so as to ferrous oxidising into ferric iron, iron chloride is added, in the moon
The dry place of airing is stood after curing certain hour, and impurity screening obtains liquid polymerization ferric sulfate;
B. attapulgite is bakeed into 40-80min at 300 DEG C -700 DEG C, 1-2h is soaked with sulfuric acid waste after cooling, filtered, water
It is washed till after neutrality and is ground, uses 150-250 mesh sieves, drying for standby;
C. step b gained attapulgite and flyash, red soil are added in ethylene glycol solution, suspension are obtained after ultrasonic disperse,
Silver nitrate, polyacrylamide VN835 are added, after immersion 2-5h, centrifugation, washing is vacuum dried under the conditions of 25-55 DEG C, obtains
Absorption polyacrylamide VN835, and carry attapulgite, flyash, the red soil mixture of silver;
D. step c gained mixture is added in step a gained liquid, 1h-6h is stirred at 30-70 DEG C, filtered, then
In 30 DEG C of -50 DEG C of drying, powdery is ground to form.
3. a kind of flyash composite polymeric ferric sulfate flocculant according to claim 2 and preparation method thereof, its feature exists
In the curing time is that 2-4 is all.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201611149585.9A CN106630057A (en) | 2016-12-14 | 2016-12-14 | Fly ash composite polyferric sulfate flocculating agent and preparation method thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201611149585.9A CN106630057A (en) | 2016-12-14 | 2016-12-14 | Fly ash composite polyferric sulfate flocculating agent and preparation method thereof |
Publications (1)
Publication Number | Publication Date |
---|---|
CN106630057A true CN106630057A (en) | 2017-05-10 |
Family
ID=58824661
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201611149585.9A Pending CN106630057A (en) | 2016-12-14 | 2016-12-14 | Fly ash composite polyferric sulfate flocculating agent and preparation method thereof |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN106630057A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109536172A (en) * | 2018-11-13 | 2019-03-29 | 南京师范大学 | A kind of material and restorative procedure of repairing organic and mercury contaminated soil |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101974566A (en) * | 2010-10-30 | 2011-02-16 | 中南大学 | Method for preparing and using polymeric flocculant polyferric silicate sulfate |
CN102491464A (en) * | 2011-11-25 | 2012-06-13 | 亿利资源集团有限公司 | Flocculating agent and preparation method thereof |
CN102627342A (en) * | 2012-04-19 | 2012-08-08 | 宁夏兴平精细化工股份有限公司 | Magnetic powder flocculating agent and application method thereof |
CN103253752A (en) * | 2013-05-29 | 2013-08-21 | 滁州友林科技发展有限公司 | High-efficiency flocculant |
CN105540805A (en) * | 2015-12-08 | 2016-05-04 | 甘肃省建材科研设计院 | Potato starch waste water macro-molecule organic matter separation treatment special-purpose flocculating agent |
-
2016
- 2016-12-14 CN CN201611149585.9A patent/CN106630057A/en active Pending
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101974566A (en) * | 2010-10-30 | 2011-02-16 | 中南大学 | Method for preparing and using polymeric flocculant polyferric silicate sulfate |
CN102491464A (en) * | 2011-11-25 | 2012-06-13 | 亿利资源集团有限公司 | Flocculating agent and preparation method thereof |
CN102627342A (en) * | 2012-04-19 | 2012-08-08 | 宁夏兴平精细化工股份有限公司 | Magnetic powder flocculating agent and application method thereof |
CN103253752A (en) * | 2013-05-29 | 2013-08-21 | 滁州友林科技发展有限公司 | High-efficiency flocculant |
CN105540805A (en) * | 2015-12-08 | 2016-05-04 | 甘肃省建材科研设计院 | Potato starch waste water macro-molecule organic matter separation treatment special-purpose flocculating agent |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109536172A (en) * | 2018-11-13 | 2019-03-29 | 南京师范大学 | A kind of material and restorative procedure of repairing organic and mercury contaminated soil |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Guo et al. | Rice straw biochar modified by aluminum chloride enhances the dewatering of the sludge from municipal sewage treatment plant | |
CN104193127B (en) | The treatment process of excess sludge after a kind of biological wastewater treatment | |
WO2016058437A1 (en) | Treatment method for deep dewatering of sludge | |
CN101797496B (en) | Preparation method of inorganic-organic compound-type adsorbent based on clinoptilolite and application for removing Cr(VI) in industrial waste water | |
CN106630081A (en) | Composite polyferric sulfate flocculant with high adsorptive property and preparation method thereof | |
CN107129016B (en) | Sewage treatment agent and preparation method thereof | |
CN103145313B (en) | Sludge conditioning agent appropriate for sludge incineration handling and conditioning method | |
CN109956690B (en) | Method for treating fly ash generated by burning household garbage in cement industry | |
CN106517467A (en) | Composite polyferric sulfate flocculating agent containing activated carbon and preparation method of composite polyferric sulfate flocculating agent | |
CN104761116B (en) | A kind of method of mud normal-temperature deep dehydration | |
CN106865655A (en) | A kind of attapulgite sewage-treating agent and preparation method thereof | |
Yang et al. | Explore the closed-loop disposal route of surplus sludge: Sludge self-circulation preparation of sludge-based biochar (SBB) to enhance sludge dewaterability | |
CN106824059A (en) | A kind of porous attapulgite clay adsorbent for treatment of dyeing wastewater and preparation method thereof | |
CN106630131B (en) | A kind of preparation method of modified attapulgite soil particle and the method for accelerating anaerobic granulation using it | |
CN114044620B (en) | Method for preparing sludge conditioner by using water supply sludge and application thereof | |
CN104724897A (en) | Sludge dewatering conditioning agent and use method thereof | |
CN101234332A (en) | Method for using sewage sludge and waste graphite to prepare activated adsorption material | |
CN106336038B (en) | A kind of processing method containing heavy metal polluted waste water | |
CN107032567B (en) | Method for deodorizing and reducing municipal sludge | |
CN104478029B (en) | A kind of water treatment agent and preparation method thereof | |
CN110776244A (en) | Method for conditioning municipal sludge by using red mud | |
CN105498552B (en) | A kind of conductive filter membrane and its preparation method and application that conductor oxidate is modified | |
CN106673159A (en) | Attapulgite-loaded modified poly-silicon ferric sulfate flocculant and preparation method thereof | |
CN106902758A (en) | A kind of preparation and application of the Graphene adsorbent of aerobic particle mud N doping | |
CN106630057A (en) | Fly ash composite polyferric sulfate flocculating agent and preparation method thereof |
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 | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20170510 |