CN106242003A - A kind of organic-inorganic composite efficient flocculant and preparation method thereof - Google Patents

A kind of organic-inorganic composite efficient flocculant and preparation method thereof Download PDF

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CN106242003A
CN106242003A CN201610912039.XA CN201610912039A CN106242003A CN 106242003 A CN106242003 A CN 106242003A CN 201610912039 A CN201610912039 A CN 201610912039A CN 106242003 A CN106242003 A CN 106242003A
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inorganic composite
organic
flocculant
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蓝文贵
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    • 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
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • 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
    • C02F1/42Treatment of water, waste water, or sewage by ion-exchange
    • 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
    • C02F1/5245Treatment 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
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/001Runoff or storm water
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/16Nature of the water, waste water, sewage or sludge to be treated from metallurgical processes, i.e. from the production, refining or treatment of metals, e.g. galvanic wastes

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  • 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)
  • Chemical Kinetics & Catalysis (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

The invention discloses a kind of organic-inorganic composite efficient flocculant and preparation method thereof, described organic-inorganic composite efficient flocculant includes aluminium polychlorid (white) (PAC), aluminum sulfate (Al2(SO4)3), PAM, slaked lime, modified fine coal, modified 4A zeolite powder, kieselguhr, sodium sulfate.The present invention provides a kind of flocculant added without hydrolysis dilution, a kind of economical, efficient, quick, broad spectrum type, energy industrialized production, without " three wastes " pollute, environmentally friendly, be harmful to human health, realize garbage recycling, to reach the environmentally friendly organic-inorganic composite flocculant of the treatment of wastes with processes of wastes against one another.

Description

A kind of organic-inorganic composite efficient flocculant and preparation method thereof
Technical field
The invention belongs to city water, sanitary sewage, field of industrial waste water treatment, particularly relate to a kind of organic and inorganic compound Mould assembly efficient flocculant and preparation method thereof.
Background technology
Along with the high speed development of China's modernization of industry process, how to improve the efficiency of water for industrial use, save valuable water Resource, and in the sustainable development of rational development of water resources application and water resource utilizes, water technology plays not Alternative important function.For source water, the purified treatment of feedwater, sanitary sewage, industrial wastewater recycling in, flocculant (comprise some and have the coagulant of agglutination, flocculation aid) is chemistry in water treatment medicament the most frequently used in water processing links, they It is broadly divided into organic polymer coargulator and the big class of inorganic polymer flocculant two.
China's inorganic flocculating agent applicating history is long, owing to low-molecular inorganic flocculant exists bigger in water treatment procedure Problem, progressively substituted by inorganic polymer flocculant, it is more effective than original flocculant much, and price the most corresponding As, thus progressively become the main flow medicament that same organic polymer coargulator is the same.But, no matter it is used alone that a kind of organic high One's share of expenses for a joint undertaking flocculant or inorganic polymer flocculant, have respective limitation, has respective pluses and minuses: 1. organic polymer Flocculant shows: building bridge for Organic substance float, it is excellent to adsorb, and flocculates excellent, and coagulation grain group is big, and formation speed is fast, sedimentation filtration Good, the pH value that applicable scope is bigger.But in operation condition and the time of hydrolysis, stability, show themselves in that hydrolysis time is long, Diluent keeping quality after hydrolysis, poor stability, must avoid during operation at a high speed and stirring of overrunning, except chromatic effect and clarity Poor.2. inorganic polymer flocculant shows: have preferable coagulation flocculating effect for inorganic matter, for the glue in float Body thing is extremely effective, and particularly when high concentrtion, performance is notable.Clarity is extremely effective, preferably removes lignin, humus etc. Color, hydrolysis time is short, the advantage that after hydrolysis, the diluent holding time is longer.But flocculate in operation condition formation condition Poor, do not have organic polymer coargulator excellent.Because sedimentation filtration speed is general, at a high speed after answer low rate mixing, adsorption activity is poor, Flocculating strength is the most weak, alumen ustum easily by Work machine strength failure, the shortcoming that the pH range of adaptation is less.
In each side such as Water purification, sanitary sewage disposal, Industrial Wastewater Treatment, valuable substance recovery and sludge treatments When face uses flocculant, it is contemplated that the kind of float, electric charge, chemical substance composition in handled water quality, surface activity The pH value of architectural characteristic, granularity, concentration and water quality, temperature, the chemical composition of concurrent, process technique, equipment etc. and select Select.Perhaps two kinds of flocculant compound with better adapting to the process of different quality, organic and inorganic two kinds of macromolecules When flocculant is used in combination, its major advantage being added effect is: 1. guarantees that 2. clarity increase the intensity of flocculation, strengthens grain 3. degree and adsorption activity improve concentrations, filter and the efficiency of lock out operation 4. accelerate to flocculate formed, precipitate, the speed of the process such as filtration Degree, simplifies technological process, and 5. the disposal ability that improve process equipment structures improves the compressibility of mud, dehydration property, 6. minimizing subsidence volumn expands the scope of effective pH value that flocculates and 7. saves processing cost, medicament expense use.
Although the most domestic research for inorganic composite floculant and patent, disclose much new technique, But their technique is all to hydrolyze, with inorganic flocculating agent, the use that is combined with each other by organic flocculant and hydrolysis, or will be each Multi-point adding after organic flocculant is compound and after the hydrolysis dilution of inorganic flocculating agent.These inorganic composite floculants are at mesh Still there is many drawbacks in front water treatment procedure, medicament movement requirement height, complex process, equipment investment greatly, process and take up an area Area is big, and operational management is complicated, and operating cost is high, it is impossible to adapt to the application of the many new water treatment facilities developed under the new situation, Cause the limitation processing market application at water.
Summary of the invention
The present invention is to solve inorganic composite floculant needs the technical problem that hydrolysis dilution adds in water processes, A kind of flocculant added without hydrolysis dilution, a kind of height that organic-inorganic flocculant is effectively combined into a kind of broad spectrum type are provided Effect, the powder flocculant of rapid flocculation.Process for water provide one can simple and quick formation than great, sedimentation is fast, wadding thing is thick Real flocculant.For this technique that water is processed, equipment, engineering, regulating tank, the scale of precipitate and separate groove can be reduced, Reduce technological process, reduce construction costs, and can directly use integration to separate precipitation apparatus.Deduct common high score Sub-flocculant etc. are various helps solidifying medicament to hydrolyze, through first, the method that dilution adds respectively, has simplified operation complexity, has managed loaded down with trivial details Engineer operation.It is an object of the invention to provide a kind of economical, efficient, quick, broad spectrum type, energy industrialized production, without " three Useless " pollute, environmentally friendly, be harmful to human health, realize garbage recycling, to reach the environmental friendliness of the treatment of wastes with processes of wastes against one another The organic-inorganic composite flocculant of type.
To achieve these goals, the technical solution used in the present invention is as follows: a kind of organic-inorganic composite efficient flocculating Agent, it is characterised in that: the raw material of described flocculant forms and content is by mass percentage:
Aluminium polychlorid (PAC): 10% 20%,
Aluminum sulfate (Al2(SO4)3): 15% 38%,
PAM:5% 15%,
Slaked lime: 10% 40%,
Modified coal ash: 3% 15%,
Modified 4A zeolite powder: 2% 15%,
Kieselguhr: 5% 10%,
Sodium sulfate: 5% 10%.
Further, described modified coal ash is the sodium hydrate aqueous solution modification through over-richness is 10% 30%;Institute Stating modified 4A zeolite powder 5% 15% is the sodium-chloride water solution modification through over-richness is 5% 20%.
Further, the preparation method of described organic-inorganic composite efficient flocculant, comprise the steps:
Step 1: be dissolved in sodium hydroxide solution by flyash, through stirring mixing, after the normal-temperature reaction of 24 hours, floating In solution, impurity foam is removed, after taking out flyash, it is not necessary to rinse, and directly air-dries and is dried, or delivers in baking box, on 150 ° of left sides Right high temperature takes out cooling after drying, i.e. prepare the modified absorption that has and help the modified coal ash of solidifying function, standby to make.
Step 2: be dissolved in sodium chloride solution by the natural zeolite powder that particle diameter is 300 mesh is through stirring mixing, little through 48 Time normal-temperature reaction after, the impurity floated in solution and foam are removed, take out zeolite powder, it is not necessary to rinse, directly air-dry dry, Or deliver in baking box, and after the high temperature of about 150 ° are dried, take out cooling, i.e. prepare modification has ion exchange, absorption point From, the modified 4A zeolite powder of catalysis, standby to make.
Step 3: it is the powder between 100 mesh 300 mesh that aluminum sulfate is ground into particle diameter, standby to make.
Step 4: account for the aluminium polychlorid (PAC) of gross weight 10% 20% with account for gross weight 15% 38% powder Aluminum sulfate is mixed by mixing apparatus, at normal temperatures and pressures by 30 turns per minute, through 10 20 minutes be thoroughly mixed, Standby to make to mixture I.
Step 5: accounting for the slaked lime of gross weight 10% 40%, accounting for the modified coal ash of gross weight 3% 15%, account for gross weight The modified 4A powdery zeolite mixing of 2% 15%, by mixing apparatus at normal temperatures and pressures, by 30 turns per minute, carries out 10 20 Minute be thoroughly mixed, obtain mixture II standby to make.
Step 6: account for gross weight 15% 70% mixture in gross weight 25% 58% mixture I and step 5 by accounting in step 4 II mixing, then put into the PAM accounting for gross weight 5% 15%, accounts for the kieselguhr of gross weight 5% 10%, then adds and account for gross weight 5% The sodium sulfate of 10%, at normal temperatures and pressures, carry out the mix and blend of 10 20 minutes by the speed of 30 turns per minute after, i.e. obtains The inorganic composite floculant of the present invention, i.e. obtains qualified finished product after weighing, packing.
Further, in described modified coal ash, modifying agent be concentration be 10% 30% sodium hydroxide solutions;Described modified 4A In zeolite powder, modifying agent be concentration be 5% 20% sodium chloride solutions.
Further, in step 1, it is necessary to flyash through the normal-temperature reaction of more than 24 hours.
Further, in step 2, it is necessary to zeolite powder through the normal-temperature reaction of more than 48 hours.
Further, in step 3, it is necessary to aluminum sulfate is ground into, through pulverizer, the powder sulfur that particle diameter is 100 mesh 300 mesh Acid aluminum.
The invention has the beneficial effects as follows: (1) present invention can realize flocculation separation, before removing from wide pH value (4 12) Processing acid adjustment alkali tune operation, waste strength without dilution, manages operation of flocculating completely at 10mg/l 4000mg/l in fact.(2) this Bright treatment effect is obvious, through the stirring of 30 seconds to 5 minutes after input, flocculation reaction just occurs, generates cotton-shaped big and solid, i.e. Make to be not easy to destroy flco through stirring reaction for a long time, without recondensing operation during dehydration, can settle at one go.(3) originally Invention product does not contains noxious substance, and safety is high.(4) using the water that the present invention processes, easily, warp is folded for the dehydration of flocculating sedimentation thing After the dehydration of spiral shell dewaterer, moisture content is between 25% 45%.(5) present invention can increase and decrease joining of product according to industry sewage situation 5, as applied in paper industry, precipitate can become regenerated resources, it is not necessary to outward transport landfill or burning disposal, can be converted into again Green material recycles.(6) using the product of the present invention, the supporting processing equipment of use can be simplified, miniaturization.Dosing time, Potion takes effect, and removes loaded down with trivial details dissolving operation from, makes disposable apparatus investment be greatly decreased, also shortened process, saving simultaneously Construction investment, operating cost etc..(7) dosage of this product is extremely low, and adding dosage is that 10ppm 350ppm does not waits (according to water The difference of matter and take the circumstances into consideration to add), when former water SS concentration is below 500mg/l, consumption is: 10ppm 30ppm, at 500mg/ Between l 1000mg/l, consumption is: 30ppm 60ppm.It is 60ppm 120mg/l when 1000mg/l 5000mg/l.? During more than 5000mg/l, consumption is 120mg 350mg/l.(8) the organic-inorganic flocculant of the present invention has production simply, raw Discharging without " three wastes " during product, garbage comprehensively recycles, and is to have excellent cost performance and the environment of broad mass market prospect The efficient flocculant of friendly.(9) product of the present invention is respectively as the advantage of novel flocculant with flocculant on the market Can be by disposable for various types of dirty substances flocculation deposition seperation with a kind of flocculant of the present invention under the conditions of Zhong.
Detailed description of the invention
Below in conjunction with the embodiment of the present invention, the technical scheme in the embodiment of the present invention is clearly and completely described, Obviously, described embodiment is only a part of embodiment of the present invention rather than whole embodiments.Based in the present invention Embodiment, the every other embodiment that those of ordinary skill in the art are obtained under not making creative work premise, all Belong to the scope of protection of the invention.
Embodiment 1:
A kind of organic-inorganic composite efficient flocculant, includes aluminium polychlorid (white) (PAC) according to the raw material of weight ratio: 10%, aluminum sulfate: 30%, PAM:12%, slaked lime: 30%, modified coal ash: 3%, modified 4A zeolite powder: 2%, kieselguhr: 5%, sulfur Acid sodium: 8%.
The preparation method of described organic-inorganic composite efficient flocculant, comprises the steps:
Step 1: be dissolved in sodium hydroxide solution by flyash, through stirring mixing, after the normal-temperature reaction of 24 hours, floating In solution, impurity foam is removed, after taking out flyash, it is not necessary to rinse, and directly air-dries and is dried, or delivers in baking box, on 150 ° of left sides Right high temperature takes out cooling after drying, i.e. prepare the modified absorption that has and help the modified coal ash of solidifying function, standby to make.
Step 2: be dissolved in sodium chloride solution by the natural zeolite powder that particle diameter is 300 mesh is through stirring mixing, little through 48 Time normal-temperature reaction after, the impurity floated in solution and foam are removed, take out zeolite powder, it is not necessary to rinse, directly air-dry dry, Or deliver in baking box, and after the high temperature of about 150 ° are dried, take out cooling, i.e. prepare modification has ion exchange, absorption point From, the modified 4A zeolite powder of catalysis, standby to make.
Step 3: it is the powder between 150 mesh 300 mesh that aluminum sulfate is ground into particle diameter, standby to make.
Step 4: the aluminum sulfate of the aluminium polychlorid (PAC) and the powder accounting for gross weight 30% that account for gross weight 10% is passed through Mixing apparatus mixes, and at normal temperatures and pressures by 30 turns per minute, through 10 20 minutes be thoroughly mixed, obtains mixture I Standby to make.
Step 5: accounting for the slaked lime of gross weight 30%, accounting for the modified coal ash of gross weight 3%, account for the modified 4A of gross weight 2% Powdery zeolite mix, by mixing apparatus at normal temperatures and pressures, by 30 turns per minute, carry out 10 20 minutes be sufficiently stirred for mix Close, obtain mixture II standby to make.
Step 6: gross weight 40% mixture I will be accounted in step 4 and account for gross weight 35% mixture II in step 5 and mix, then Put into the PAM accounting for gross weight 12%, account for the kieselguhr of gross weight 5%, then add the sodium sulfate accounting for gross weight 8%, at normal temperature and pressure Under, carry out the mix and blend of 10 20 minutes by the speed of 30 turns per minute after, it is combined into slightly acid organo-mineral complexing wadding Solidifying agent.
When the flocculant obtained in embodiment 1 is for processing mining area containing arsenic former water, being 7.1 at PH, former water containing arsenic concentration is The 300ml waste water of 0.103mg/L, after only need to adding this flocculant 5mg, the homogenizer by 300 turns per minute stirs 2 points After 40 seconds, produce flocculation sediment, after supernatant passes through filter paper filtering, by detection, be 0.005mg/l containing arsenic concentration, clearance It is 95%.
Embodiment 2:
A kind of organic-inorganic composite efficient flocculant, includes aluminium polychlorid (white) (PAC) according to the raw material of weight ratio: 12%, aluminum sulfate: 38%, PAM:15%, slaked lime: 20%, modified coal ash: 3%, modified 4A zeolite powder: 2%, kieselguhr: 5%, sulfur Acid sodium: 5%.
The preparation method of described organic-inorganic composite efficient flocculant, comprises the steps:
Step 1: be dissolved in sodium hydroxide solution by flyash, through stirring mixing, after the normal-temperature reaction of 24 hours, floating In solution, impurity foam is removed, after taking out flyash, it is not necessary to rinse, and directly air-dries and is dried, or delivers in baking box, on 150 ° of left sides Right high temperature takes out cooling after drying, i.e. prepare the modified absorption that has and help the modified coal ash of solidifying function, standby to make.
Step 2: be dissolved in sodium chloride solution by the natural zeolite powder that particle diameter is 300 mesh is through stirring mixing, little through 48 Time normal-temperature reaction after, the impurity floated in solution and foam are removed, take out zeolite powder, it is not necessary to rinse, directly air-dry dry, Or deliver in baking box, and after the high temperature of about 150 ° are dried, take out cooling, i.e. prepare modification has ion exchange, absorption point From, the modified 4A zeolite powder of catalysis, standby to make.
Step 3: it is the powder between 100 mesh 300 mesh that aluminum sulfate is ground into particle diameter, standby to make.
Step 4: the aluminum sulfate of the aluminium polychlorid (PAC) and the powder accounting for gross weight 38% that account for gross weight 12% is passed through Mixing apparatus mixes, and at normal temperatures and pressures by 30 turns per minute, through 10 20 minutes be thoroughly mixed, obtains mixture I Standby to make.
Step 5: accounting for the slaked lime of gross weight 20%, accounting for the modified coal ash of gross weight 3%, account for the modified 4A of gross weight 2% Powdery zeolite mix, by mixing apparatus at normal temperatures and pressures, by 30 turns per minute, carry out 10 20 minutes be sufficiently stirred for mix Close, obtain mixture II standby to make.
Step 6: gross weight 50% mixture I will be accounted in step 4 and account for gross weight 25% mixture II in step 5 and mix, then Put into the PAM accounting for gross weight 15%, account for the kieselguhr of gross weight 5%, then add the sodium sulfate accounting for gross weight 5%, at normal temperature and pressure Under, carry out the mix and blend of 10 20 minutes by the speed of 30 turns per minute after, it is combined into slightly acid organo-mineral complexing wadding Solidifying agent.
When the flocculant obtained in embodiment 2 is for processing ceramics factory's waste water, it is that 630mg/l, BOD are in former water SS concentration 12.4mg/l, PH be 7.2 300ml waste water in only need to add after this flocculant 5mg through by the high-speed stirred of 300 turns per minute Machine stirs 2 points after 30 seconds, and SS concentration reduces to 8.6mg/l, and clearance is 98.64%, and BOD reduces to 0.12, and clearance is 99.98% (recording out after filter paper filters with the supernatant after precipitation).
Embodiment 3:
A kind of organic-inorganic composite efficient flocculant, includes aluminium polychlorid (white) (PAC) according to the raw material of weight ratio: 10%, aluminum sulfate: 20%, PAM:15%, slaked lime: 40%, modified coal ash: 3%, modified 4A zeolite powder: 2%, kieselguhr: 5%, sulfur Acid sodium: 5%.
The preparation method of described organic-inorganic composite efficient flocculant, comprises the steps:
Step 1: be dissolved in sodium hydroxide solution by flyash, through stirring mixing, after the normal-temperature reaction of 24 hours, floating In solution, impurity foam is removed, after taking out flyash, it is not necessary to rinse, and directly air-dries and is dried, or delivers in baking box, on 150 ° of left sides Right high temperature takes out cooling after drying, i.e. prepare the modified absorption that has and help the modified coal ash of solidifying function, standby to make.
Step 2: be dissolved in sodium chloride solution by the natural zeolite powder that particle diameter is 300 mesh is through stirring mixing, little through 48 Time normal-temperature reaction after, the impurity floated in solution and foam are removed, take out zeolite powder, it is not necessary to rinse, directly air-dry dry, Or deliver in baking box, and after the high temperature of about 150 ° are dried, take out cooling, i.e. prepare modification has ion exchange, absorption point From, the modified 4A zeolite powder of catalysis, standby to make.
Step 3: it is the powder between 100 mesh 300 mesh that aluminum sulfate is ground into particle diameter, standby to make.
Step 4: the aluminum sulfate of the aluminium polychlorid (PAC) and the powder accounting for gross weight 20% that account for gross weight 10% is passed through Mixing apparatus mixes, and at normal temperatures and pressures by 30 turns per minute, through 10 20 minutes be thoroughly mixed, obtains mixture I Standby to make.
Step 5: accounting for the slaked lime of gross weight 40%, accounting for the modified coal ash of gross weight 3%, account for the modified 4A of gross weight 2% Powdery zeolite mix, by mixing apparatus at normal temperatures and pressures, by 30 turns per minute, carry out 10 20 minutes be sufficiently stirred for mix Close, obtain mixture II standby to make.
Step 6: gross weight 30% mixture I will be accounted in step 4 and account for gross weight 45% mixture II in step 5 and mix, then Put into the PAM accounting for gross weight 15%, account for the kieselguhr of gross weight 5%, then add the sodium sulfate accounting for gross weight 5%, at normal temperature and pressure Under, carry out the mix and blend of 10 20 minutes by the speed of 30 turns per minute after, it is combined into slightly alkalescence organo-mineral complexing wadding Solidifying agent.
When the flocculant obtained in embodiment 3 is for processing community life effluent sewerage, it is 6.9 at pH value, former water SS Concentration be 765mg/l, BOD concentration be that 964mg/l, h-hexane is extracted oil in material (mg/l) water out and is divided into the 300ml of 48mg/l dirty After having stirred 3 minutes by the homogenizer of 300 turns per minute after only need to adding this flocculant 6mg in water, supernatant passes through Filtering to detect after cotton pad filters and draw, SS concentration is 15mg/l, and clearance is 99%, and BOD concentration is 187mg/l, and clearance is 80%, 0.02mg/l reduced to by oil point, and clearance is 99%.
Embodiment 4:
A kind of organic-inorganic composite efficient flocculant, includes aluminium polychlorid (white) (PAC) according to the raw material of weight ratio: 10%, aluminum sulfate: 28%, PAM:12%, slaked lime: 35%, modified coal ash: 3%, modified 4A zeolite powder: 2%, kieselguhr: 5%, sulfur Acid sodium: 5%.
The preparation method of described organic-inorganic composite efficient flocculant, comprises the steps:
Step 1: be dissolved in sodium hydroxide solution by flyash, through stirring mixing, after the normal-temperature reaction of 24 hours, floating In solution, impurity foam is removed, after taking out flyash, it is not necessary to rinse, and directly air-dries and is dried, or delivers in baking box, on 150 ° of left sides Right high temperature takes out cooling after drying, i.e. prepare the modified absorption that has and help the modified coal ash of solidifying function, standby to make.
Step 2: be dissolved in sodium chloride solution by the natural zeolite powder that particle diameter is 300 mesh is through stirring mixing, little through 48 Time normal-temperature reaction after, the impurity floated in solution and foam are removed, take out zeolite powder, it is not necessary to rinse, directly air-dry dry, Or deliver in baking box, and after the high temperature of about 150 ° are dried, take out cooling, i.e. prepare modification has ion exchange, absorption point From, the modified 4A zeolite powder of catalysis, standby to make.
Step 3: it is the powder between 100 mesh 300 mesh that aluminum sulfate is ground into particle diameter, standby to make.
Step 4: the aluminum sulfate of the aluminium polychlorid (PAC) and the powder accounting for gross weight 28% that account for gross weight 10% is passed through Mixing apparatus mixes, and at normal temperatures and pressures by 30 turns per minute, through 10 20 minutes be thoroughly mixed, obtains mixture I Standby to make.
Step 5: accounting for the slaked lime of gross weight 35%, accounting for the modified coal ash of gross weight 3%, account for the modified 4A of gross weight 2% Powdery zeolite mix, by mixing apparatus at normal temperatures and pressures, by 30 turns per minute, carry out 10 20 minutes be sufficiently stirred for mix Close, obtain mixture II standby to make.
Step 6: gross weight 38% mixture I will be accounted in step 4 and account for gross weight 40% mixture II in step 5 and mix, then Put into the PAM accounting for gross weight 12%, account for the kieselguhr of gross weight 5%, then add the sodium sulfate accounting for gross weight 5%, at normal temperature and pressure Under, carry out the mix and blend of 10 20 minutes by the speed of 30 turns per minute after, it is combined into slightly alkalescence organo-mineral complexing wadding Solidifying agent.
The flocculant obtained in embodiment 4, for processing the Metal Cutting lapping liquid of machinery processing factory, is 6.8 at pH value, Former water BOD concentration is that in 486mg/l, h-hexane extraction material (mg/l) water, oil is divided in the 300ml sewage of 1856mg/l only need After being stirred 3 minutes by the homogenizer of 300 turns per minute after adding this flocculant 6mg, the supernatant after precipitating 5 minutes, Detecting that BOD concentration reduces to 5.8mg/l after filter cotton pad filters, clearance is 98.81%, and concentration of oil is 1.6mg/l, goes Except rate is 99.9%.
Above-described embodiment is only several embodiments preferred for this invention, should not be assumed that the present invention is only capable of taking above-mentioned Several case study on implementation, all technical characteristics limited based on right of the present invention, and combine the cognitive model of those skilled in the art Enclose the technical scheme that interior be capable of routine is altered or modified, and in the basis limited without departing from appended claims Invention, makes various changes in the form and details and all should be considered to fall protection scope of the present invention the present invention In.

Claims (7)

1. an organic-inorganic composite efficient flocculant, it is characterised in that: described organic-inorganic composite efficient flocculant Raw material composition and by mass percentage content be:
Aluminium polychlorid (PAC): 10% 20%,
Aluminum sulfate (Al2(SO4)3): 15% 38%,
PAM:5% 15%,
Slaked lime: 10% 40%,
Modified coal ash: 3% 15%,
Modified 4A zeolite powder: 2% 15%,
Kieselguhr: 5% 10%,
Sodium sulfate: 5% 10%.
A kind of organic-inorganic composite efficient flocculant the most according to claim 1, it is characterised in that: described modified fine coal Ash is the sodium hydrate aqueous solution modification through over-richness is 10% 30%;Described modified 4A zeolite powder 5% 15% be through Concentration is the sodium-chloride water solution modification of 5% 20%.
3. the preparation method of an organic-inorganic composite efficient flocculant as claimed in claim 1, it is characterised in that: include Following steps:
Step 1: be dissolved in sodium hydroxide solution by flyash, through stirring mixing, after the normal-temperature reaction of 24 hours, floating In solution, impurity foam is removed, after taking out flyash, it is not necessary to rinse, and directly air-dries and is dried, or delivers in baking box, on 150 ° of left sides Right high temperature takes out cooling after drying, i.e. prepare the modified absorption that has and help the modified coal ash of solidifying function, standby to make;
Step 2: be dissolved in sodium chloride solution by the natural zeolite powder that particle diameter is 300 mesh, through stirring mixing, through 48 hours After normal-temperature reaction, the impurity floated in solution and foam are removed, takes out zeolite powder, it is not necessary to rinse, directly air-dry and be dried, or send To baking box, after the high temperature of about 150 ° are dried, take out cooling, i.e. prepare and modified there is ion exchange, adsorbing separation, urge Change the modified 4A zeolite powder of function, standby to make;
Step 3: it is the powder between 100 mesh 300 mesh that aluminum sulfate is ground into particle diameter, standby to make;
Step 4: account for the aluminium polychlorid (PAC) of gross weight 10% 20% with account for gross weight 15% 38% the sulphuric acid of powder Aluminum is mixed by mixing apparatus, at normal temperatures and pressures by 30 turns per minute, through 10 20 minutes be thoroughly mixed, is mixed Compound I is standby to make;
Step 5: accounting for the slaked lime of gross weight 10% 40%, accounting for the modified coal ash of gross weight 3% 15%, account for gross weight 2% The modified 4A powdery zeolite mixing of 15%, by mixing apparatus at normal temperatures and pressures, by 30 turns per minute, carries out 10 20 minutes Be thoroughly mixed, obtain mixture II standby to make;
Step 6: account for gross weight 15% 70% mixture II in gross weight 25% 58% mixture I and step 5 mix accounting in step 4 Close, then put into the PAM accounting for gross weight 5% 15%, account for the kieselguhr of gross weight 5% 10%, then add and account for gross weight 5% 10% Sodium sulfate, at normal temperatures and pressures, carry out the mix and blend of 10 20 minutes by the speed of 30 turns per minute after, i.e. obtain this Bright inorganic composite floculant, i.e. obtains qualified finished product after weighing, packing.
The preparation method of a kind of organic-inorganic composite efficient flocculant the most according to claim 3, it is characterised in that: institute State in modified coal ash, modifying agent be concentration be 10% 30% sodium hydroxide solutions;In described modified 4A zeolite powder, modifying agent is Concentration is 5% 20% sodium chloride solutions.
The preparation method of a kind of organic-inorganic composite efficient flocculant the most according to claim 3, it is characterised in that: step In rapid 1, it is necessary to flyash through the normal-temperature reaction of more than 24 hours.
The preparation method of a kind of organic-inorganic composite efficient flocculant the most according to claim 3, it is characterised in that: step In rapid 2, it is necessary to zeolite powder through the normal-temperature reaction of more than 48 hours.
The preparation method of a kind of organic-inorganic composite efficient flocculant the most according to claim 3, it is characterised in that: step In rapid 3, it is necessary to aluminum sulfate is ground into, through pulverizer, the powder aluminum sulfate that particle diameter is 100 mesh 300 mesh.
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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106830241A (en) * 2017-01-11 2017-06-13 刘成才 A kind of compound for sewage disposal and preparation method thereof
CN108264137A (en) * 2017-12-12 2018-07-10 安徽国泰化工有限公司 A kind of organic-inorganic compound high-efficient flocculant
CN109775828A (en) * 2019-03-12 2019-05-21 美丽国土(北京)生态环境工程技术研究院有限公司 Composite flocculation agent and its preparation method and application
CN111392804A (en) * 2020-02-25 2020-07-10 国电新能源技术研究院有限公司 Water purification method by using fly ash
CN111689617A (en) * 2020-07-02 2020-09-22 苏州中材建设有限公司 Dry-process cement production line wastewater treatment system
CN112142128A (en) * 2019-06-26 2020-12-29 广西沣登环境科技有限公司 Garbage treatment degradation agent, flocculant and garbage concentrated solution treatment method capable of directly discharging
CN113149167A (en) * 2021-04-25 2021-07-23 郑州沃煌环保技术有限公司 Compounding method of inorganic multifunctional sewage treatment coagulant

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102616905A (en) * 2012-04-06 2012-08-01 厦门市大净环保科技有限公司 Organic and inorganic composite high-efficiency flocculating agent and preparation method thereof
CN103253751A (en) * 2013-05-24 2013-08-21 杨雪飞 Inorganic-organic multi-element composite flocculant, and preparation method and application thereof
CN104229957A (en) * 2013-06-24 2014-12-24 张家领 Compound flocculant taking natural minerals as main components

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102616905A (en) * 2012-04-06 2012-08-01 厦门市大净环保科技有限公司 Organic and inorganic composite high-efficiency flocculating agent and preparation method thereof
CN103253751A (en) * 2013-05-24 2013-08-21 杨雪飞 Inorganic-organic multi-element composite flocculant, and preparation method and application thereof
CN104229957A (en) * 2013-06-24 2014-12-24 张家领 Compound flocculant taking natural minerals as main components

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
于晓彩: "《粉煤灰与造纸废水资源化技术的研究》", 31 August 2013, 辽宁教育出版社 *
张玉龙等: "《水处理剂配方设计与实例》", 31 May 2011, 中国纺织出版社 *
舒万艮: "《有色金属精细化工产品生产与应用》", 31 December 1995, 中南工业大学出版社 *

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106830241A (en) * 2017-01-11 2017-06-13 刘成才 A kind of compound for sewage disposal and preparation method thereof
CN108264137A (en) * 2017-12-12 2018-07-10 安徽国泰化工有限公司 A kind of organic-inorganic compound high-efficient flocculant
CN109775828A (en) * 2019-03-12 2019-05-21 美丽国土(北京)生态环境工程技术研究院有限公司 Composite flocculation agent and its preparation method and application
CN112142128A (en) * 2019-06-26 2020-12-29 广西沣登环境科技有限公司 Garbage treatment degradation agent, flocculant and garbage concentrated solution treatment method capable of directly discharging
CN111392804A (en) * 2020-02-25 2020-07-10 国电新能源技术研究院有限公司 Water purification method by using fly ash
CN111689617A (en) * 2020-07-02 2020-09-22 苏州中材建设有限公司 Dry-process cement production line wastewater treatment system
CN113149167A (en) * 2021-04-25 2021-07-23 郑州沃煌环保技术有限公司 Compounding method of inorganic multifunctional sewage treatment coagulant

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