CN108017127A - A kind of nano-high molecule carboxymethyl chitosan sewage treatment drug and processing method - Google Patents

A kind of nano-high molecule carboxymethyl chitosan sewage treatment drug and processing method Download PDF

Info

Publication number
CN108017127A
CN108017127A CN201711122124.7A CN201711122124A CN108017127A CN 108017127 A CN108017127 A CN 108017127A CN 201711122124 A CN201711122124 A CN 201711122124A CN 108017127 A CN108017127 A CN 108017127A
Authority
CN
China
Prior art keywords
parts
sewage
water
sanitary sewage
waste 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.)
Withdrawn
Application number
CN201711122124.7A
Other languages
Chinese (zh)
Inventor
张金风
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.)
Qingdao Zhuo Sen Biological Engineering Co Ltd
Original Assignee
Qingdao Zhuo Sen Biological Engineering 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 Qingdao Zhuo Sen Biological Engineering Co Ltd filed Critical Qingdao Zhuo Sen Biological Engineering Co Ltd
Priority to CN201711122124.7A priority Critical patent/CN108017127A/en
Publication of CN108017127A publication Critical patent/CN108017127A/en
Withdrawn legal-status Critical Current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
    • C02F1/5263Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using natural chemical 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
    • 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
    • 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
    • C02F1/542Phosphorus 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
    • C02F1/54Treatment 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
    • C02F9/00Multistage treatment of water, waste water or sewage
    • 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
    • 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
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • 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
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • 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
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • C02F1/32Treatment of water, waste water, or sewage by irradiation with ultraviolet light
    • 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
    • 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
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/103Arsenic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/105Phosphorus compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/12Halogens or halogen-containing compounds
    • C02F2101/14Fluorine or fluorine-containing compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/36Organic compounds containing halogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage

Abstract

The present invention is a kind of nano-high molecule carboxymethyl chitosan sanitary sewage disposal medicament and processing method, is related to technical field of waste water processing, is made of the component of following weight percentage:15 25 parts of carboxymethyl chitosan, 5 10 parts of sodium alginate, 5 10 parts of mandruka graphene, 25 30 parts of chaff ketone resin, modified 15 20 parts of seaweed acidic group fiber, etc..Modification of chitosan based sols of the present invention, using fiber as the molding carrier of modification of chitosan based sols, nano-titanium dioxide is grafted on surface and increases its surface area ratio, the poly- silicon fluoride of inorganic cation is used in high surface area outer layer, Electrostatic Absorption is formed with organic anion polyene acid amides, ensure that stability and fixing of the material on the basis of high surface area ratio.By the method, and add medicament and multistage abatement processes are carried out to sanitary sewage, positive effect, realize recycling for water resource.

Description

A kind of nano-high molecule carboxymethyl chitosan sewage treatment drug and processing method
Invention field
The invention belongs to technical field of waste water processing, relates in particular to a kind of nano-high molecule carboxymethyl chitosan life Sewage treatment drug and domestic sewage processing method.
Background technology
With the increase of wastewater treatment rate and processing depth, sludge discharge is in the speed increasing with annual more than 10-15% It is long, but supporting specific resistance to filtration is but without acquirement greater advance.Due to the reasons such as technology, policy, most domestic city City's sewage sludge is all to utilize landfill stabilization mode, does not carry out harmless treatment, the secondary pollution problem of sludge is extremely serious. A large amount of landfills of high water content sludge cause to take valuable land resource, so that many cities can not find landfill yard.Sludge oozes Filtrate becomes the pollution sources of underground water in many areas, and landfill yard also then becomes air into mosquito breeding ground, landfill gas Pollution sources.Developed country's specific resistance to filtration such as Europe and North America progressively turns to the resource recycling profit based on sludge drying Based on, burning gradually reduces, and the ratio of Sludge landfill is gradually reduced, or even forbids sludge landfill.And sludge drying is Sludge realizes innoxious, minimizing, the key link of recycling treatment disposal.
Existing natural energy resources mainly include water energy, wind energy, solar energy, tide energy, biomass energy etc., wherein water resource Most of area of the earth is occupied, is one of energy that we depend on for existence, as the continuous improvement of living standard, life are dirty Water is more and more, but does not catch up with expanding rapidly with water scale but to the disposal ability of waste water, it is impossible to effectively realizes science Recycle water resource.
The content of the invention
In view of this, the present invention provides a kind of nano-high molecule carboxymethyl chitosan sanitary sewage disposal medicament and processing Method, by the method, and adds medicament and multistage abatement processes is carried out to sanitary sewage, positive effect, realize water resource Recycle.
To reach above-mentioned purpose, the technical solution used in the present invention is:
A kind of nano-high molecule carboxymethyl chitosan sanitary sewage disposal medicament, by following weight percentage into packet Into:15-25 parts of carboxymethyl chitosan, 5-10 parts of sodium alginate, 5-10 parts of mandruka graphene, 25-30 parts of chaff ketone resin, Modified 15-20 parts of seaweed acidic group fiber, 60-80 parts of inorganic salts water purification agent, 10-20 parts of sodium dichloro cyanurate, polyacrylamide 10-25 parts of amine, 10-25 parts of activated carbon, 5-15 parts of hexapotassium, 4-12 parts of dispersant, 1-4.5 parts of sodium acid carbonate, 0.5-1.5 parts of adipic acid, 3-7 parts of zeolite, 8-12 parts of diatomite.The modification seaweed acidic group fiber preparation method is:
Alginic acid, 70% hydrochloric acid are taken according to volume ratio 1:1 mixing, and the deionized water for adding 6 times of gross weight is heated to 110 DEG C mixed liquor A stirred evenly, cellulose acetate tow is added in mixed liquor A, is matched as 1ml:0.2g, keep the heating-up temperature after Continuous stirring 25min is to uniform that seaweed acidic group fiber liquid is spare.
Preferably, in the preferred embodiment, the inorganic salts water purification agent for polyaluminium salts, aluminium salt, zinc salt, One or more mixtures with arbitrary proportion in molysite, calcium salt, polymeric ferric salt, magnesium salts, boron salt and silicon systems salt.
Preferably, in the preferred embodiment, the Molecular Weight for Polyacrylamide is more than 10000.
A kind of purifying domestic sewage processing method, comprises the following steps:
(1) pollutant suspend in water and floating is filtered and recycled by sanitary sewage filter plant logical first, The biologies such as the total fish of water body are filtered at the same time, avoid it from then passing through the water body by filtering solid with water body flow Liquid separation equipment, and the sediments such as the bulky grain pond sludge in water body, humus are recycled, then remaining water body is continued Flowed in purifying water process water system system;
Sewage purification processing system is re-fed into, sanitary sewage enters grid well through pipe network, then flows into setting pot certainly, just sinks Pond, uses undissolved suspended solid and floating impurity in physical methods of filtration waste water;
(2) sanitary sewage after filtering is entered into biological respinse processing pond by water pump lifting, is gone using biological method depth Except the organic pollution in waste water;
(3) coagulative precipitation tank is passed through, the sanitary sewage disposal medicament is uniformly sprinkling upon in waste water according to the above ratio, with 80-140r/min stirs 60-120s, it is come into full contact with reaction, removes, separates in waste water in dissolving, the pollution of colloidal state Thing;
(4) waste water enters secondary settling tank after separating, and stands 30-40min, the supernatant of secondary settling tank is filtered, sterilize after it is up to standard Discharge, the excess sludge of secondary settling tank is filtered, concentration, is discharged into septic tank after dehydration and makees other processing.
Further included in the purifying domestic sewage process method step (4):Waste water enters pretreatment chamber by feed space Interior, the clear water in spraying device is rinsed to entering the indoor sewage of pretreatment, passes through the filtering twice of filter screen The concentration of organic matter in sewage substantially reduces, and then discharges the silt after filtering by sewage draining exit, it is pretreated after water Entered again by sewage conduct in mud chamber, neutralize material inlet and the indoor sewage of neutralization precipitation is inserted into mud chamber, Start by motor, the ion in sewage is fully reacted with reaction raw materials, then the sewage after reaction is passed through it is right in MVR evaporators Sewage and secondary steam evaporation, will be unable to evaporation after sewage it is carried out by ultra violet sterilizer it is last disinfect, The sludge in sewage is set to reach discharge standard.
Preferably, in the preferred embodiment, the purifying domestic sewage processing method depends on sanitary sewage Cleaning treatment system, the purifying domestic sewage processing system collect pipe network, grille well, setting pot, primary sedimentation tank, life including sewage Thing reaction treatment pond, coagulative precipitation tank, secondary settling tank, filtering ponds, disinfecting tank, tank, drainage system, wherein each several part it Between be sequentially connected in order by pipeline.
Preferably, in the preferred embodiment, the grid includes middle grid and fine fack, the middle grid and The angle of the water surface is 75 degree.
Preferably, in the preferred embodiment, the biological respinse processing pond includes anaerobic pond, catalytic oxidation Pond.
Preferably, in the preferred embodiment, the dosage of the sanitary sewage disposal medicament according to the above ratio For 20-30mg/l.
Relative to the prior art, beneficial effects of the present invention:The present invention provides a kind of nano-high molecule methylol shell to gather Sugared sanitary sewage disposal medicament and processing method, by the method, and add medicament and multistage abatement processes are carried out to sanitary sewage, Positive effect, realize recycling for water resource.
Modification of chitosan based sols of the present invention, using fiber as the molding carrier of modification of chitosan based sols, by nanometer Titanium dioxide is grafted on surface and increases its surface area ratio, and the poly- silicon fluoride of inorganic cation is used in high surface area outer layer, and organic Cationic polyalkylene acid amides forms Electrostatic Absorption, ensure that stability and fixing of the material on the basis of high surface area ratio.
The sanitary sewage disposal medicament of offer makes particle by suction-operated, charge neutrality effect and bridge formation suction-operated Big flocculate is condensed into, accelerates the sedimentation of particle in suspension.Inorganic component and organic component are with covalently bonded in the medicament Close, it is with good stability, it is (turbidity, organic matter in such as source water and sewage, thin that water-borne glue body particulate matter can not only be removed Bacterium, virus etc.), phosphorus, fluorine, arsenic etc., can also efficiently remove the dissolubility that the molecular weight that traditional flocculant is difficult to remove is less than 500 Pollutant (such as Diclofenac, niflumic acid, PFOA), so as to substantially increase flocculation ability, has and fast and efficiently flocculates Effect.
By analyzing the main component in sanitary sewage, waste water is pointedly purified using method, using physical method, Biological method and chemical method are combined as the processing method of sanitary wastewater, and the division of labor is clear and definite, multistage decontaminates, positive effect, realizes Waste water reuse.
Embodiment
Technical solution of the present invention is further described with reference to specific embodiment.
Embodiment 1:
The embodiment of the present invention 1 provides a kind of nano-high molecule carboxymethyl chitosan sanitary sewage disposal medicament, by with The component composition of lower weight percentage:15 parts of carboxymethyl chitosan, 5 parts of sodium alginate, 5 parts of mandruka graphene, chaff ketone 25 parts of urea formaldehyde, modified 15 parts of seaweed acidic group fiber, 60 parts of inorganic salts water purification agent, 10 parts of sodium dichloro cyanurate, polypropylene 10 parts of acid amides, 10 parts of activated carbon, 5 parts of hexapotassium, 4 parts of dispersant, 1 part of sodium acid carbonate, 0.5 part of adipic acid, boiling 3 parts of stone, 8 parts of diatomite.
The modification seaweed acidic group fiber preparation method is:
Alginic acid, 70% hydrochloric acid are taken according to volume ratio 1:1 mixing, and the deionized water for adding 6 times of gross weight is heated to 110 DEG C mixed liquor A stirred evenly, cellulose acetate tow is added in mixed liquor A, is matched as 1ml:0.2g, keep the heating-up temperature after Continuous stirring 25min is to uniform that seaweed acidic group fiber liquid is spare.
Inorganic salts water purification agent is polyaluminium salts, aluminium salt and calcium salt with the mixture of arbitrary proportion.
Molecular Weight for Polyacrylamide is more than 10000.
A kind of purifying domestic sewage processing method, comprises the following steps:
(1) pollutant suspend in water and floating is filtered and recycled by sanitary sewage filter plant logical first, The biologies such as the total fish of water body are filtered at the same time, avoid it from then passing through the water body by filtering solid with water body flow Liquid separation equipment, and the sediments such as the bulky grain pond sludge in water body, humus are recycled, then remaining water body is continued Flowed in purifying water process water system system;
Sewage purification processing system is re-fed into, sanitary sewage enters grid well through pipe network, then flows into setting pot certainly, just sinks Pond, uses undissolved suspended solid and floating impurity in physical methods of filtration waste water;
(2) sanitary sewage after filtering is entered into biological respinse processing pond by water pump lifting, is gone using biological method depth Except the organic pollution in waste water;
(3) coagulative precipitation tank is passed through, sanitary sewage disposal medicament is uniformly sprinkling upon in waste water, 60s is stirred with 80r/min, It is come into full contact with reaction, remove, separate in waste water in dissolving, the pollutant of colloidal state;
(4) waste water enters secondary settling tank after separating, and stands 30min, the supernatant of secondary settling tank is filtered, sterilize after row up to standard Put, the excess sludge of secondary settling tank is filtered, concentration, is discharged into septic tank after dehydration and makees other processing.
Further included in the purifying domestic sewage process method step (4):Waste water enters pretreatment chamber by feed space Interior, the clear water in spraying device is rinsed to entering the indoor sewage of pretreatment, passes through the filtering twice of filter screen The concentration of organic matter in sewage substantially reduces, and then discharges the silt after filtering by sewage draining exit, it is pretreated after water Entered again by sewage conduct in mud chamber, neutralize material inlet and the indoor sewage of neutralization precipitation is inserted into mud chamber, Start by motor, the ion in sewage is fully reacted with reaction raw materials, then the sewage after reaction is passed through it is right in MVR evaporators Sewage and secondary steam evaporation, will be unable to evaporation after sewage it is carried out by ultra violet sterilizer it is last disinfect, The sludge in sewage is set to reach discharge standard.
Purifying domestic sewage processing method depends on purifying domestic sewage processing system, purifying domestic sewage processing system bag Include sewage collect pipe network, grille well, setting pot, primary sedimentation tank, biological respinse processing pond, coagulative precipitation tank, secondary settling tank, filtering ponds, It is sequentially connected in order by pipeline between disinfecting tank, tank, drainage system, wherein each several part.
Grid includes middle grid and fine fack, and the angle of middle grid and the water surface is 75 degree.
Biological respinse processing pond includes anaerobic pond, contact-oxidation pool.
The dosage of sanitary sewage disposal medicament is 20mg/l.
Embodiment 2:
The embodiment of the present invention 2 provides a kind of nano-high molecule carboxymethyl chitosan sanitary sewage disposal medicament, by with The component composition of lower weight percentage:18 parts of carboxymethyl chitosan, 8 parts of sodium alginate, 8 parts of mandruka graphene, chaff ketone 27 parts of urea formaldehyde, modified 18 parts of seaweed acidic group fiber, 80 parts of inorganic salts water purification agent, 20 parts of sodium dichloro cyanurate, polypropylene 25 parts of acid amides, 25 parts of activated carbon, 15 parts of hexapotassium, 12 parts of dispersant, 4.5 parts of sodium acid carbonate, adipic acid 1.5 Part, 7 parts of zeolite, 12 parts of diatomite.
The modification seaweed acidic group fiber preparation method is:
Alginic acid, 70% hydrochloric acid are taken according to volume ratio 1:1 mixing, and the deionized water for adding 6 times of gross weight is heated to 110 DEG C mixed liquor A stirred evenly, cellulose acetate tow is added in mixed liquor A, is matched as 1ml:0.2g, keep the heating-up temperature after Continuous stirring 25min is to uniform that seaweed acidic group fiber liquid is spare.
Inorganic salts water purification agent is calcium salt, polymeric ferric salt, molysite, the mixture with arbitrary proportion.
Molecular Weight for Polyacrylamide is more than 10000.
A kind of purifying domestic sewage processing method, comprises the following steps:
(1) pollutant suspend in water and floating is filtered and recycled by sanitary sewage filter plant logical first, The biologies such as the total fish of water body are filtered at the same time, avoid it from then passing through the water body by filtering solid with water body flow Liquid separation equipment, and the sediments such as the bulky grain pond sludge in water body, humus are recycled, then remaining water body is continued Flowed in purifying water process water system system;
Sewage purification processing system is re-fed into, sanitary sewage enters grid well through pipe network, then flows into setting pot certainly, just sinks Pond, uses undissolved suspended solid and floating impurity in physical methods of filtration waste water;
(2) sanitary sewage after filtering is entered into biological respinse processing pond by water pump lifting, is gone using biological method depth Except the organic pollution in waste water;
(3) coagulative precipitation tank is passed through, sanitary sewage disposal medicament is uniformly sprinkling upon in waste water, is stirred with 140r/min 120s, makes it come into full contact with reaction, removes, separates in waste water in dissolving, the pollutant of colloidal state;
(4) waste water enters secondary settling tank after separating, and stands 40min, the supernatant of secondary settling tank is filtered, sterilize after row up to standard Put, the excess sludge of secondary settling tank is filtered, concentration, is discharged into septic tank after dehydration and makees other processing.
Further included in the purifying domestic sewage process method step (4):Waste water enters pretreatment chamber by feed space Interior, the clear water in spraying device is rinsed to entering the indoor sewage of pretreatment, passes through the filtering twice of filter screen The concentration of organic matter in sewage substantially reduces, and then discharges the silt after filtering by sewage draining exit, it is pretreated after water Entered again by sewage conduct in mud chamber, neutralize material inlet and the indoor sewage of neutralization precipitation is inserted into mud chamber, Start by motor, the ion in sewage is fully reacted with reaction raw materials, then the sewage after reaction is passed through it is right in MVR evaporators Sewage and secondary steam evaporation, will be unable to evaporation after sewage it is carried out by ultra violet sterilizer it is last disinfect, The sludge in sewage is set to reach discharge standard.
Purifying domestic sewage processing method depends on purifying domestic sewage processing system, purifying domestic sewage processing system bag Include sewage collect pipe network, grille well, setting pot, primary sedimentation tank, biological respinse processing pond, coagulative precipitation tank, secondary settling tank, filtering ponds, It is sequentially connected in order by pipeline between disinfecting tank, tank, drainage system, wherein each several part.
Grid includes middle grid and fine fack, and the angle of middle grid and the water surface is 75 degree.
Biological respinse processing pond includes anaerobic pond, contact-oxidation pool.
The dosage of sanitary sewage disposal medicament is 30mg/l.
Embodiment 3:
The embodiment of the present invention 3 provides a kind of nano-high molecule carboxymethyl chitosan sanitary sewage disposal medicament, by with The component composition of lower weight percentage:25 parts of carboxymethyl chitosan, 10 parts of sodium alginate, 10 parts of mandruka graphene, chaff 30 parts of ketone resin, modified 20 parts of seaweed acidic group fiber, 70 parts of inorganic salts water purification agent, 15 parts of sodium dichloro cyanurate, poly- third 17 parts of acrylamide, 17 parts of activated carbon, 10 parts of hexapotassium, 8 parts of dispersant, 2.7 parts of sodium acid carbonate, 1 part of adipic acid, 5 parts of zeolite, 10 parts of diatomite.The modification seaweed acidic group fiber preparation method is:
Alginic acid, 70% hydrochloric acid are taken according to volume ratio 1:1 mixing, and the deionized water for adding 6 times of gross weight is heated to 110 DEG C mixed liquor A stirred evenly, cellulose acetate tow is added in mixed liquor A, is matched as 1ml:0.2g, keep the heating-up temperature after Continuous stirring 25min is to uniform that seaweed acidic group fiber liquid is spare.
Inorganic salts water purification agent is polyaluminium salts, aluminium salt, calcium salt are with the mixture of arbitrary proportion.
Molecular Weight for Polyacrylamide is more than 10000.
A kind of purifying domestic sewage processing method, comprises the following steps:
(1) pollutant suspend in water and floating is filtered and recycled by sanitary sewage filter plant logical first, The biologies such as the total fish of water body are filtered at the same time, avoid it from then passing through the water body by filtering solid with water body flow Liquid separation equipment, and the sediments such as the bulky grain pond sludge in water body, humus are recycled, then remaining water body is continued Flowed in purifying water process water system system;
Sewage purification processing system is re-fed into, sanitary sewage enters grid well through pipe network, then flows into setting pot certainly, just sinks Pond, uses undissolved suspended solid and floating impurity in physical methods of filtration waste water;
(2) sanitary sewage after filtering is entered into biological respinse processing pond by water pump lifting, is gone using biological method depth Except the organic pollution in waste water;
(3) coagulative precipitation tank is passed through, sanitary sewage disposal medicament is uniformly sprinkling upon in waste water, 90s is stirred with 110r/min, It is come into full contact with reaction, remove, separate in waste water in dissolving, the pollutant of colloidal state;
(4) waste water enters secondary settling tank after separating, and stands 35min, the supernatant of secondary settling tank is filtered, sterilize after row up to standard Put, the excess sludge of secondary settling tank is filtered, concentration, is discharged into septic tank after dehydration and makees other processing.
Further included in the purifying domestic sewage process method step (4):Waste water enters pretreatment chamber by feed space Interior, the clear water in spraying device is rinsed to entering the indoor sewage of pretreatment, passes through the filtering twice of filter screen The concentration of organic matter in sewage substantially reduces, and then discharges the silt after filtering by sewage draining exit, it is pretreated after water Entered again by sewage conduct in mud chamber, neutralize material inlet and the indoor sewage of neutralization precipitation is inserted into mud chamber, Start by motor, the ion in sewage is fully reacted with reaction raw materials, then the sewage after reaction is passed through it is right in MVR evaporators Sewage and secondary steam evaporation, will be unable to evaporation after sewage it is carried out by ultra violet sterilizer it is last disinfect, The sludge in sewage is set to reach discharge standard.
Purifying domestic sewage processing method depends on purifying domestic sewage processing system, purifying domestic sewage processing system bag Include sewage collect pipe network, grille well, setting pot, primary sedimentation tank, biological respinse processing pond, coagulative precipitation tank, secondary settling tank, filtering ponds, It is sequentially connected in order by pipeline between disinfecting tank, tank, drainage system, wherein each several part.
Grid includes middle grid and fine fack, and the angle of middle grid and the water surface is 75 degree.
Biological respinse processing pond includes anaerobic pond, contact-oxidation pool.
The dosage of sanitary sewage disposal medicament is 25mg/l.
With purifying domestic sewage processing method provided by the invention, sanitary sewage disposal medicine made from addition embodiment 1-3 Agent, the part index number for obtaining sanitary sewage before and after the processing are as shown in table 1:
Table 1:The part index number of sanitary sewage before and after the processing
Above-mentioned sanitary sewage is after chemicals treatment produced by the present invention, and last effluent quality, meets after testing《Cities and towns are dirty Water treatment plant's pollutant emission standard》(GB18918-2002) pollutant highest allows concentration of emission wherein primary standard limit value.

Claims (5)

1. a kind of nano-high molecule carboxymethyl chitosan sanitary sewage disposal medicament, it is characterised in that contained by following weight percent The component composition of amount:15-25 parts of carboxymethyl chitosan, 5-10 parts of sodium alginate, 5-10 parts of mandruka graphene, chaff keto-aldehyde tree 25-30 parts of fat, modified 15-20 parts of seaweed acidic group fiber, 60-80 parts of inorganic salts water purification agent, sodium dichloro cyanurate 10-20 Part, 10-25 parts of polyacrylamide, 10-25 parts of activated carbon, 5-15 parts of hexapotassium, 4-12 parts of dispersant, bicarbonate 1-4.5 parts of sodium, 0.5-1.5 parts of adipic acid, 3-7 parts of zeolite, 8-12 parts of diatomite:The modification seaweed acidic group fiber preparation side Formula is:
Alginic acid, 70% hydrochloric acid are taken according to volume ratio 1:1 mixing, and the deionized water for adding 6 times of gross weight is heated to 110 DEG C and stirs Uniform mixed liquor A is mixed, cellulose acetate tow is added in mixed liquor A, is matched as 1ml:0.2g, keeps the heating-up temperature to continue to stir It is spare to uniform seaweed acidic group fiber liquid to mix 25min.
2. sanitary sewage disposal medicament according to claim 1, it is characterised in that:The inorganic salts water purification agent is polymerization One or more in aluminium salt, aluminium salt, zinc salt, molysite, calcium salt, polymeric ferric salt, magnesium salts, boron salt and silicon systems salt are with arbitrary proportion Mixture.
3. sanitary sewage disposal medicament according to claim 1, it is characterised in that:The Molecular Weight for Polyacrylamide is More than 10000.
4. a kind of purifying domestic sewage processing method, it is characterised in that comprise the following steps:
(1) pollutant suspend in water and floating is filtered and recycled by sanitary sewage filter plant logical first, at the same time The biologies such as the total fish of water body are filtered, avoid it that the water body by filtering then is passed through solid-liquid point with water body flow Recycled from equipment, and by sediments such as the bulky grain pond sludge in water body, humus, then continued remaining water body in water Flowing in purified treatment water system system;
Sewage purification processing system is re-fed into, sanitary sewage enters grid well through pipe network, then flows into setting pot, primary sedimentation tank certainly, Use undissolved suspended solid and floating impurity in physical methods of filtration waste water;
(2) sanitary sewage after filtering is entered into biological respinse processing pond by water pump lifting, is removed using biological method depth useless Organic pollution in water;
(3) coagulative precipitation tank is passed through, the sanitary sewage disposal medicament is uniformly sprinkling upon in waste water according to the above ratio, with 80- 140r/min stirs 60-120s, it is come into full contact with reaction, removes, separates in waste water in dissolving, the pollutant of colloidal state;
(4) waste water enters secondary settling tank after separating, and stands 30-40min, the supernatant of secondary settling tank is filtered, sterilize after qualified discharge, The excess sludge of secondary settling tank is filtered, concentration, is discharged into septic tank after dehydration and makees other processing.
5. purifying domestic sewage processing method according to claim 4, it is characterised in that:The purifying domestic sewage processing Method and step further includes in (4):Waste water is entered in pretreatment chamber by feed space, and the clear water in spraying device is pre- to entering Handle indoor sewage to be rinsed, substantially reduced by the concentration for filtering the organic matter in sewage twice of filter screen, Then the silt after filtering is discharged by sewage draining exit, it is pretreated after water entered again by sewage conduct in mud chamber, Neutralize material inlet and the indoor sewage of neutralization precipitation inserted into mud chamber, start by motor, make ion in sewage with it is anti- Answer raw material fully to react, then the sewage after reaction is passed through in MVR evaporators to sewage and secondary steam evaporation, will be unable to evaporate Sewage afterwards it is carried out by ultra violet sterilizer it is last disinfect, enable the sludge in sewage reach discharge mark It is accurate.
CN201711122124.7A 2017-11-14 2017-11-14 A kind of nano-high molecule carboxymethyl chitosan sewage treatment drug and processing method Withdrawn CN108017127A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201711122124.7A CN108017127A (en) 2017-11-14 2017-11-14 A kind of nano-high molecule carboxymethyl chitosan sewage treatment drug and processing method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201711122124.7A CN108017127A (en) 2017-11-14 2017-11-14 A kind of nano-high molecule carboxymethyl chitosan sewage treatment drug and processing method

Publications (1)

Publication Number Publication Date
CN108017127A true CN108017127A (en) 2018-05-11

Family

ID=62079825

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201711122124.7A Withdrawn CN108017127A (en) 2017-11-14 2017-11-14 A kind of nano-high molecule carboxymethyl chitosan sewage treatment drug and processing method

Country Status (1)

Country Link
CN (1) CN108017127A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109205748A (en) * 2018-10-30 2019-01-15 成都其其小数科技有限公司 A kind of flocculant and preparation method for heavy metal-polluted water process
CN109319908A (en) * 2018-11-07 2019-02-12 上海纳米技术及应用国家工程研究中心有限公司 Modification of chitosan-sodium alginate composite flocculation agent preparation method and products thereof and application
CN112279347A (en) * 2020-09-08 2021-01-29 广州户户通科技发展有限公司 Efficient domestic sewage treatment agent and preparation method and application thereof
CN112442378A (en) * 2020-12-02 2021-03-05 青岛科技大学 Adsorbent for heavy metal contaminated soil and preparation method and application thereof

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104759253A (en) * 2015-04-14 2015-07-08 中国广州分析测试中心 Graphene sponge used for enriching heavy metals or removing pollutants in water and preparation method of graphene sponge
CN105217842A (en) * 2015-10-30 2016-01-06 无锡市嘉邦电力管道厂 A kind of waste water treatment process
CN105948349A (en) * 2016-07-19 2016-09-21 北京农学院 Garden water system water circulating purifying technology
CN106007217A (en) * 2016-07-14 2016-10-12 苏州天擎电子通讯有限公司 Sewage treatment method
CN106188798A (en) * 2016-07-11 2016-12-07 苏州锐特捷化工制品有限公司 A kind of compound dust collecting graphene nano modified nano fiber and production method thereof
CN106179238A (en) * 2016-07-08 2016-12-07 天津工业大学 A kind of porous nano-fibre of rapid heavy metal ion adsorption and preparation method thereof

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104759253A (en) * 2015-04-14 2015-07-08 中国广州分析测试中心 Graphene sponge used for enriching heavy metals or removing pollutants in water and preparation method of graphene sponge
CN105217842A (en) * 2015-10-30 2016-01-06 无锡市嘉邦电力管道厂 A kind of waste water treatment process
CN106179238A (en) * 2016-07-08 2016-12-07 天津工业大学 A kind of porous nano-fibre of rapid heavy metal ion adsorption and preparation method thereof
CN106188798A (en) * 2016-07-11 2016-12-07 苏州锐特捷化工制品有限公司 A kind of compound dust collecting graphene nano modified nano fiber and production method thereof
CN106007217A (en) * 2016-07-14 2016-10-12 苏州天擎电子通讯有限公司 Sewage treatment method
CN105948349A (en) * 2016-07-19 2016-09-21 北京农学院 Garden water system water circulating purifying technology

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109205748A (en) * 2018-10-30 2019-01-15 成都其其小数科技有限公司 A kind of flocculant and preparation method for heavy metal-polluted water process
CN109319908A (en) * 2018-11-07 2019-02-12 上海纳米技术及应用国家工程研究中心有限公司 Modification of chitosan-sodium alginate composite flocculation agent preparation method and products thereof and application
CN112279347A (en) * 2020-09-08 2021-01-29 广州户户通科技发展有限公司 Efficient domestic sewage treatment agent and preparation method and application thereof
CN112442378A (en) * 2020-12-02 2021-03-05 青岛科技大学 Adsorbent for heavy metal contaminated soil and preparation method and application thereof

Similar Documents

Publication Publication Date Title
Hidayaturrahman et al. A study on characteristics of microplastic in wastewater of South Korea: Identification, quantification, and fate of microplastics during treatment process
Tang et al. Microplastics removal through water treatment plants: Its feasibility, efficiency, future prospects and enhancement by proper waste management
CN108017127A (en) A kind of nano-high molecule carboxymethyl chitosan sewage treatment drug and processing method
Bodzek et al. Removal of organic compounds from municipal landfill leachate in a membrane bioreactor
CN106865639A (en) A kind of water body and in-situ sediment remediation agent and restorative procedure
CN102040294A (en) Treatment method for circulating water sewerage and reverse osmosis concentrated water
Anju et al. Exploring the use of orange peel and neem leaf powder as alternative coagulant in treatment of dairy wastewater
CN106167342A (en) A kind of biological medicine waste water nitrogen phosphorus processing means and processing method thereof
CN208362111U (en) A kind of urban sewage treatment system
Mukhlish et al. Removal of reactive dye from aqueous solution using coagulation–flocculation coupled with adsorption on papaya leaf
CN106630310A (en) Urban black and odorous water body treatment method
CN105906164A (en) Method for removing ammonia nitrogen in waste water
Bendida et al. Treatment of domestic wastewater from the town of Bechar by a sand filter (sand of Beni Abbes Bechar Algeria)
CN102718295A (en) Compound medicament for treating coking wastewater and preparation method thereof
CN108059297A (en) A kind of carbon nano tube compound material sewage treatment drug and processing method
CN108751598A (en) A kind of city domestic sewage treatment process
CN107188340A (en) A kind of high-concentration culture waste water handling process
CN104973722B (en) A kind of dyeing and printing sewage processing system
CN105884144A (en) Process for efficiently treating sewage
CN208717084U (en) Water environment cleaning treatment system
CN110294569A (en) A kind of processing method of polyurethane production waste water
CN101585642A (en) Sewage treatment systems based on artificial swamp
CN211198959U (en) Hazardous waste leachate treatment system
CN108017226A (en) A kind of high molecular nanometer sewage treatment drug and processing method
Melián Sustainable Wastewater Treatment Systems

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
WW01 Invention patent application withdrawn after publication

Application publication date: 20180511

WW01 Invention patent application withdrawn after publication