CN111875116A - Paint wastewater treatment composition and treatment method - Google Patents

Paint wastewater treatment composition and treatment method Download PDF

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Publication number
CN111875116A
CN111875116A CN202010792935.3A CN202010792935A CN111875116A CN 111875116 A CN111875116 A CN 111875116A CN 202010792935 A CN202010792935 A CN 202010792935A CN 111875116 A CN111875116 A CN 111875116A
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China
Prior art keywords
paint
treatment agent
weight
parts
paint wastewater
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202010792935.3A
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Chinese (zh)
Inventor
李静静
孙芳
唐俊花
褚建波
刘岩
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 Zhongcheng Sanxiongdi Environmental Engineering Co ltd
Original Assignee
Qingdao Zhongcheng Sanxiongdi Environmental Engineering Co ltd
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Publication date
Application filed by Qingdao Zhongcheng Sanxiongdi Environmental Engineering Co ltd filed Critical Qingdao Zhongcheng Sanxiongdi Environmental Engineering Co ltd
Priority to CN202211189253.9A priority Critical patent/CN115385489A/en
Priority to CN202010792935.3A priority patent/CN111875116A/en
Publication of CN111875116A publication Critical patent/CN111875116A/en
Pending legal-status Critical Current

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    • 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
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/285Treatment of water, waste water, or sewage by sorption using synthetic organic 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/286Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
    • 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
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
    • 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
    • C02F1/56Macromolecular compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment 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
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/42Treatment of water, waste water, or sewage by ion-exchange
    • C02F2001/425Treatment of water, waste water, or sewage by ion-exchange using cation exchangers
    • 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
    • C02F2101/20Heavy metals or heavy metal 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
    • 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
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32

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  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

The invention discloses a paint wastewater treatment composition and a treatment method, wherein the paint wastewater treatment method specifically comprises the following steps: collecting paint wastewater in a sewage tank, adding a sewage treatment agent A into the paint wastewater, then adding a sewage treatment agent B into the paint wastewater, adding a sewage treatment agent C after the sewage treatment agent is completely dispersed and paint sewage is accompanied by a small amount of precipitate, uniformly stirring, then generating a large amount of precipitate, and settling and filtering to remove precipitated impurities. The paint wastewater treatment method can remove organic polymers and heavy metals in the paint wastewater, and can convert micromolecular organic matters in the paint wastewater into carbon dioxide and water.

Description

Paint wastewater treatment composition and treatment method
Technical Field
The invention relates to a paint wastewater treatment composition and a treatment method.
Background
The production and application of paint have a long history, and China has used paint for thousands of years ago, and the paint used at that time is prepared from paint liquid collected from lacquer trees into natural paint. The main components of the modern paint comprise the following five major parts: (1) oil material: including drying oils and semi-drying oils, which are one of the main film-forming substances; (2) resin: including natural and artificial resins, are also part of the main film-forming material; (3) pigment: the pigment comprises coloring pigment, extender pigment and antirust pigment, and the specific varieties are quite various and are secondary film-forming substances; (4) diluting materials: comprises solvent and thinner, which is used to dissolve the above-mentioned material and adjust the consistency, and is auxiliary film-forming material; (5) auxiliary materials: comprises a drier, a curing agent, a plasticizer and a moisture-proof agent, and also belongs to an auxiliary film-forming substance.
Modern paint coating operation mostly uses a spraying technology, the spraying process usually oversprays in order to obtain due product effects, and 20-60% of paint cannot be attached to products and scatters in a spraying room. In order to maintain a normal working environment on the spot and to protect the health of workers, a wet paint mist removing system, i.e., water, is often used to remove excess paint. The composition of paint determines the composition of the paint waste water. The waste water has various organic matters, complex components, high COD content and certain toxicity.
The paint spraying waste water contains a large amount of paint slag, and the paint slag is formed by mixing oil, resin, a solvent, an auxiliary agent and the like. Thereby leading the water quality to have the characteristics of stickiness, peculiar smell, heavy color and the like. The traditional paint wastewater treatment method comprises the following steps: 1. the biochemical treatment is adopted, a certain amount of chemical agents are added into the wastewater, and the wastewater is treated by a series of processes such as a water collecting adjusting tank, a grid, neutralization coagulation, air floatation, hydrolytic acidification adjustment, an oxidation ditch, a secondary sedimentation tank, an aeration biological filter tank, effluent and the like. 2. The paint wastewater is treated by adopting a filter, a settling tank and a filter pressing mode, and the treatment method has the advantages that high-viscosity substances and wastewater easily block elements, the element replacement and operation costs are high, and the reliability is low. 3. Adopt traditional paint flocculating agent, remove to paint sediment and glue, suspend the back and salvage or adopt and scrape the sediment machine and salvage by the artifical surface of water, this kind of processing method sediment is handled incompletely, can't thoroughly clear away to the bottom of the pool, causes the cascade cabinet circulating pump to block up easily and influence the spraying effect, and paint fog is easily got rid of from the gas vent and is caused secondary pollution, and the environmental protection is hardly up to standard, and running cost is higher. Today, the environmental pollution is concerned, the traditional paint spraying wastewater treatment method is too simple, and a plurality of harmful substances cannot be removed, so that the discharge standard of industrial wastewater cannot be met. A truly scientific and effective treatment method for paint spraying wastewater is to add water treatment chemicals into the water. Only in this way, harmful substances and pollutants in the paint wastewater can be completely separated, and the water quality perspective, the pH value, the impurity content, the odor, the COD and the like can reach the industrial wastewater discharge standard required by the state.
The company applies for a patent in 2018: a paint wastewater treatment method comprises the following steps: collecting paint wastewater in a sewage tank, adding a sewage treatment agent A into the paint wastewater, then adding a sewage treatment agent B into the paint wastewater, adding a sewage treatment agent C after the sewage treatment agent is completely dispersed and paint sewage is accompanied by a small amount of precipitate, uniformly stirring, then generating a large amount of precipitate, and settling and filtering to remove precipitated impurities. However, the effects of total soluble solids, total petroleum content, heavy metal content, chemical oxygen demand, etc. treated by the treatment method are not good enough, and further improvement is needed.
Disclosure of Invention
In order to solve the technical problems, the invention provides a paint wastewater treatment composition, which consists of a wastewater treatment agent A, a wastewater treatment agent B and a wastewater treatment agent C, wherein the wastewater treatment agent A consists of 100 parts by weight of strong base, 2-10 parts by weight of a dispersing agent and 5-10 parts by weight of an anionic surfactant;
the sewage treatment agent B consists of 100 parts by weight of inorganic flocculant, 5-10 parts by weight of filler, 1-10 parts by weight of polyquaternium and 10-20 parts by weight of water-soluble calcium salt;
the sewage treatment agent C is composed of a polypropylene flocculant.
The invention also provides a paint wastewater treatment method, which specifically comprises the following steps: collecting paint wastewater in a sewage tank, adding a sewage treatment agent A into the paint wastewater, then adding a sewage treatment agent B into the paint wastewater, adding a sewage treatment agent C after the sewage treatment agent is completely dispersed and paint sewage is accompanied by a small amount of precipitate, uniformly stirring, generating a large amount of precipitate, and settling and filtering to remove precipitated impurities;
the sewage treatment agent A consists of 100 parts by weight of strong base, 2-10 parts by weight of dispersant and 5-10 parts by weight of anionic surfactant;
the sewage treatment agent B consists of 100 parts by weight of inorganic flocculant, 5-10 parts by weight of filler, 1-10 parts by weight of polyquaternium and 10-20 parts by weight of water-soluble calcium salt;
the sewage treatment agent C is composed of a polypropylene flocculant.
The using amount of the sewage treatment agent A is 0.1-3% of the mass of the paint wastewater.
The using amount of the sewage treatment agent B is 0.5-3% of the mass of the paint wastewater.
The using amount of the sewage treatment agent C is 0.1-1% of the mass of the paint wastewater.
The anionic surfactant is one or more of naphthalene sulfonate formaldehyde condensate, lignosulfonate and dodecyl sulfonate.
The polyquaternium is selected from one or more of polyquaternium-6, polyquaternium-7, polyquaternium-42 and polyquaternium-21.
The filler is selected from one or more of bentonite, pyrophyllite and montmorillonite.
The inorganic flocculant is one or more selected from polyaluminium chloride, polyaluminium sulfate, polyaluminium ferric chloride, polyaluminium ferric silicate and aluminium hydroxychloride.
The polypropylene flocculant is selected from one or more of polyacrylamide, sodium polyacrylate and potassium polyacrylate.
The paint wastewater treatment method has the advantages that three different sewage treatment agents A, B and C are adopted to be matched for use, so that macromolecular organic matters, heavy metals and micromolecular organic matters in paint wastewater are removed, the A is added, so that the sewage primarily adsorbs the heavy metals by using an anionic surfactant under the alkaline condition that the pH is 7-9, the macromolecular organic matters are removed by using an inorganic flocculant, the micromolecular organic matters are removed by using an adsorptive filler, the heavy metal ions are adsorbed by using a cation exchange type filler, and the filler and the macromolecular organic matters are further flocculated by using a polypropylene flocculant, so that the macromolecular organic matters, the heavy metals and the micromolecular organic matters are removed. Compared with other patents, the removal efficiency is more efficient by adopting the scheme of the invention.
Detailed Description
Unless defined otherwise, all technical and scientific terms used herein have the same meaning as commonly understood by one of ordinary skill in the art to which this invention belongs. In case of conflict, the present specification, including definitions, will control.
The quality of the treated paint sewage is evaluated by adopting the national standard of wastewater discharge town sewer water quality standard (GB/T31962-. The quality of the water is evaluated mainly by measuring the PH value, the total soluble solid, the total petroleum content, the heavy metal content and the chemical oxygen demand.
Example 1
The paint wastewater treatment method specifically comprises the following steps: collecting paint wastewater in a sewage tank, adding a sewage treatment agent A (100 parts by weight of strong base, 5 parts by weight of dispersing agent and 8 parts by weight of anionic surfactant) into the paint wastewater to enable the pH value of the paint wastewater to be 7-9, then adding 2wt% of a sewage treatment agent B (100 parts by weight of inorganic flocculant, 8 parts by weight of filler, 5 parts by weight of polyquaternium and 15 parts by weight of water-soluble calcium salt) into the paint wastewater, adding 1wt% of a sewage treatment agent C (polypropylene flocculant) into the paint wastewater after the sewage treatment agent is completely dispersed and the paint wastewater is accompanied by a small amount of precipitate, uniformly stirring, generating a large amount of precipitate, and settling and filtering to remove precipitated impurities.
The pH value of the purified water is 7.5-7.8, the total soluble solid is 200mg/L, the total petroleum content is 0.5mg/L, the heavy metal content is less than 0.05mg/L, and the chemical oxygen demand is less than or equal to 8mg/L (COD).
Example 2
The paint wastewater treatment method specifically comprises the following steps: collecting paint wastewater in a sewage tank, adding a sewage treatment agent A (100 parts by weight of strong base, 7 parts by weight of dispersing agent and 4 parts by weight of anionic surfactant) into the paint wastewater to enable the pH value of the paint wastewater to be 7-9, then adding 2wt% of a sewage treatment agent B (100 parts by weight of inorganic flocculant, 7 parts by weight of filler, 6 parts by weight of polyquaternium and 17 parts by weight of water-soluble calcium salt) into the paint wastewater, adding 1wt% of a sewage treatment agent C (polypropylene flocculant) into the paint wastewater after the sewage treatment agent is completely dispersed and the paint wastewater is accompanied by a small amount of precipitate, uniformly stirring, generating a large amount of precipitate, and settling and filtering to remove precipitated impurities.
The pH value of the purified water is 7.5-7.8, the total soluble solid is 240mg/L, the total petroleum content is 0.8mg/L, the heavy metal content is less than 0.08mg/L, and the chemical oxygen demand is less than or equal to 9mg/L (COD).
Comparative example 1
Compared with the example 1, the sewage treatment agent A is not used, the pH value of the purified water is 7.5-7.8, the total soluble solid is 600mg/L, the total petroleum content is 5mg/L, the heavy metal content is less than 0.5mg/L, and the chemical oxygen demand is less than or equal to 30mg/L (COD).
Comparative example 2
Compared with the example 1, the sewage treatment agent B is not used, the pH value of the purified water is 7.5-7.8, the total soluble solid is 540mg/L, the total petroleum content is 3mg/L, the heavy metal content is less than 0.3mg/L, and the chemical oxygen demand is less than or equal to 18mg/L (COD).
Comparative example 3
Compared with the example 1, the sewage treatment agent C is not used, the PH value of the purified water is 7.5-7.8, the total soluble solid is 400mg/L, the total petroleum content is 1.2mg/L, the heavy metal content is less than 0.09mg/L, and the chemical oxygen demand is less than or equal to 12mg/L (COD).
The above description is only a preferred embodiment of the present invention, and is not intended to limit the scope of the present invention. All equivalent changes and modifications made according to the disclosure of the present invention are covered by the scope of the claims of the present invention.

Claims (10)

1. A paint wastewater treatment composition comprises a wastewater treatment agent A, a wastewater treatment agent B and a wastewater treatment agent C, wherein the wastewater treatment agent A comprises 100 parts by weight of strong base, 2-10 parts by weight of a dispersing agent and 5-10 parts by weight of an anionic surfactant;
the sewage treatment agent B consists of 100 parts by weight of inorganic flocculant, 5-10 parts by weight of filler, 1-10 parts by weight of polyquaternium and 10-20 parts by weight of water-soluble calcium salt;
the sewage treatment agent C is composed of a polypropylene flocculant.
2. The paint wastewater treatment method is characterized by comprising the following steps: collecting paint wastewater in a sewage tank, adding a sewage treatment agent A into the paint wastewater, then adding a sewage treatment agent B into the paint wastewater, adding a sewage treatment agent C after the sewage treatment agent is completely dispersed and paint sewage is accompanied by a small amount of precipitate, uniformly stirring, generating a large amount of precipitate, and settling and filtering to remove precipitated impurities;
the sewage treatment agent A consists of 100 parts by weight of strong base, 2-10 parts by weight of dispersant and 5-10 parts by weight of anionic surfactant;
the sewage treatment agent B consists of 100 parts by weight of inorganic flocculant, 5-10 parts by weight of filler, 1-10 parts by weight of polyquaternium and 10-20 parts by weight of water-soluble calcium salt;
the sewage treatment agent C is composed of a polypropylene flocculant.
3. The paint wastewater treatment method according to claim 2, wherein the amount of the sewage treatment agent A is 0.1-3% of the mass of the paint wastewater.
4. The paint wastewater treatment method according to claim 2, wherein the amount of the sewage treatment agent B is 0.5-3% by mass of the paint wastewater.
5. The paint wastewater treatment method according to claim 2, wherein the amount of the sewage treatment agent C is 0.1-1% by mass of the paint wastewater.
6. The paint wastewater treatment method according to claim 2, wherein the anionic surfactant is one or more of naphthalene sulfonate formaldehyde condensate, lignosulfonate and dodecyl sulfonate.
7. The paint wastewater treatment method according to claim 2, wherein the polyquaternium is one or more selected from polyquaternium-6, polyquaternium-7, polyquaternium-42 and polyquaternium-21.
8. The paint wastewater treatment method according to claim 2, wherein the filler is one or more selected from bentonite, pyrophyllite and montmorillonite.
9. The paint wastewater treatment method according to claim 2, wherein the inorganic flocculant is one or more selected from polyaluminium chloride, polyaluminium sulfate, polyaluminium ferric chloride, polyaluminium ferric silicate and aluminum hydroxychloride.
10. The paint wastewater treatment method according to claim 2, wherein the polypropylene flocculant is one or more selected from polyacrylamide, sodium polyacrylate and potassium polyacrylate.
CN202010792935.3A 2020-08-10 2020-08-10 Paint wastewater treatment composition and treatment method Pending CN111875116A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
CN202211189253.9A CN115385489A (en) 2020-08-10 2020-08-10 Paint wastewater treatment composition and application thereof in paint wastewater treatment
CN202010792935.3A CN111875116A (en) 2020-08-10 2020-08-10 Paint wastewater treatment composition and treatment method

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Application Number Priority Date Filing Date Title
CN202010792935.3A CN111875116A (en) 2020-08-10 2020-08-10 Paint wastewater treatment composition and treatment method

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113979573A (en) * 2021-12-28 2022-01-28 莱阳市春帆漆业有限责任公司 Coating waste filtering device

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102992534A (en) * 2011-09-16 2013-03-27 常熟科勒有限公司 Paint wastewater treatment method
CN103601279A (en) * 2013-11-29 2014-02-26 天津市双洁化工技术有限公司 Spray paint waste water treatment agent and treatment method thereof
CN108975577A (en) * 2018-08-20 2018-12-11 青岛众诚三兄弟环境工程有限公司 A kind of Paint wastewater treatment method
CN111217434A (en) * 2019-12-03 2020-06-02 广州越海生态环境科技有限公司 High-efficiency flocculant and preparation method thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102992534A (en) * 2011-09-16 2013-03-27 常熟科勒有限公司 Paint wastewater treatment method
CN103601279A (en) * 2013-11-29 2014-02-26 天津市双洁化工技术有限公司 Spray paint waste water treatment agent and treatment method thereof
CN108975577A (en) * 2018-08-20 2018-12-11 青岛众诚三兄弟环境工程有限公司 A kind of Paint wastewater treatment method
CN111217434A (en) * 2019-12-03 2020-06-02 广州越海生态环境科技有限公司 High-efficiency flocculant and preparation method thereof

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113979573A (en) * 2021-12-28 2022-01-28 莱阳市春帆漆业有限责任公司 Coating waste filtering device

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