CN110372174A - A kind of sludge conditioner and its application - Google Patents
A kind of sludge conditioner and its application Download PDFInfo
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- CN110372174A CN110372174A CN201910705666.XA CN201910705666A CN110372174A CN 110372174 A CN110372174 A CN 110372174A CN 201910705666 A CN201910705666 A CN 201910705666A CN 110372174 A CN110372174 A CN 110372174A
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/02—Biological treatment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/14—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
- C02F11/147—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents using organic substances
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
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- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Health & Medical Sciences (AREA)
- Molecular Biology (AREA)
- Treatment Of Sludge (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
The invention discloses a kind of sludge conditioner and its application, the sludge conditioner includes following component by mass fraction: 30-40 parts of porous adsorption carrier, 20-25 parts of biological enzyme material, 25-30 parts of flocculation aid, 10-15 parts of regulator, 10-15 parts of flocculant.Sludge conditioner of the present invention can carry out deep dehydration processing to sludge, and flocculation settling velocity is fast, effect is good, and dosage is not higher than sludge butt 10%, and TDS amplification is lower than 60% less than 10%, moisture content of the cake, alternative traditional handicraft CaO and FeCl3Combination, and preparation is simple, at low cost, it is without secondary pollution, it can be widely applied to the processing of the sludge dehydrating and dryings such as all types of industries and life, treated, and sludge can be according to different regions actual features, can be directly used for a variety of disposal options such as compost, agricultural soil, flower planting, with good application prospect with market prospects.
Description
Technical field
The invention belongs to sludge dewatering technical fields, and in particular to a kind of sludge conditioner and its application.
Background technique
With the continuous quickening of Chinese Urbanization level, municipal sewage treatment amount is continuously improved, and sludge yield is therewith not yet
It is disconnected to increase.Since the moisture content of sludge is high (reaching as high as 99.5%), complicated component not only contains a large amount of organic matters, but also contains
Harmful heavy metal, pathogenic microorganism etc., and dehydration property is poor cause sludge to stack bulky, to subsequent specific resistance to filtration and
Transport brings inconvenience and processing cost is greatly improved.Therefore, the deep dehydration of sludge has become for specific resistance to filtration
Important link.
Currently, sludge conditioner is mainly used for during the sludge conditioning before sludge dewatering, acted on by compression double electric layer,
Absorption electricity in cooperation use, adsorption bridging effect and net catch and roll up sweep act on change mud granule property, to cause sludge
In moisture be easily separated out, be conducive to sludge dewatering subsequent depths reason.However the type of sludge conditioner is more, often
Sludge conditioner mainly has three classes, i.e., inorganic sludge conditioner, organic polymer sludge conditioner and biological sludge conditioning
Agent.The applicating history of inorganic sludge conditioner is the most remote and application range is relatively broad, preparation work extensive with raw material sources
The advantages that skill is simple and price is relatively cheap, but the dosage of inorganic sludge conditioner is usually more, and sludge dewatering effect
Also limited, while the use of a large amount of inorganic sludge conditioners also can cause environmental pollution and influence.Compared to inorganic sludge tune
Agent is managed, organic polymer sludge conditioner is few with added amount of chemical, sludge formation alumen ustum is big, sludge settling property is excellent and contains
The low advantage of water rate, but there is also production costs higher, price costly the disadvantages of.Biological sludge conditioner has safe nothing
Poison, the advantages that being easily degraded by microorganisms, is without secondary pollution, but that there are dosages is larger, make and use higher cost, vulnerable to
The disadvantages of noxious material interferes, largely limits its application in practical projects.
Summary of the invention
For the above problem in the presence of the prior art, the present invention provides a kind of sludge conditioner and its applications.This
Invention sludge conditioner can carry out deep dehydration processing to sludge, and flocculation settling velocity is fast, effect is good, and preparation process is simply easy
It is capable, at low cost, it is without secondary pollution, with good application prospect with market prospects, sufficiently realize minimizing, the nothing of Treatment of Sludge
Evilization and resource utilization.
In order to achieve the above objectives, the present invention takes following technical scheme:
Sludge conditioner of the present invention includes following component by mass fraction:
30-40 parts of porous adsorption carrier, 20-25 parts of biological enzyme material, 25-30 parts of flocculation aid, 10-15 parts of regulator, wadding
It is agent 10-15 parts solidifying.
Further preferably, 30 parts of porous adsorption carrier, 20 parts of biological enzyme material, 25 parts of flocculation aid, 15 parts of regulator, wadding
Solidifying 15 parts of agent.
The porous adsorption carrier is by zeolite powder, flyash, the short fibre of stalk, maize cob meal, diatomite, attapulgite, sea
At least three kinds mixing composition in afrodite powder, and each component quality is impartial.
The biological enzyme material is by cellulase, protease, pectase, catalase, lysozyme, amylase, fat
At least three kinds mixing composition in enzyme, and each component quality is impartial.
The flocculation aid is made of magnesium salts and silicate, and each component quality is 1:1.
Preferably, the magnesium salts is made of the mixing of the ratio of magnesia and magnesium sulfate 0.5:1.5 in mass ratio;The silicic acid
Salt is made of alumina silicate, calcium silicates and sodium metasilicate 1:1:1 in mass ratio mixing.
The regulator includes sodium carbonate and/or sodium bicarbonate.
The flocculant is cationic modified starch, cationic polyacrylamide, sodium carboxymethylcellulose, poly dimethyl two
At least one of allyl ammonium chloride, polyethyleneimine.
The application method of sludge conditioner of the present invention, includes the following steps:
Step 1: each component for forming porous adsorption carrier being matched by mass fraction and is uniformly mixed, then biological enzyme will be formed
The each component of material is matched after mixing by mass fraction, and composition mixture A is mixed evenly with porous adsorption carrier;
Step 2: being matched by respective mass fraction, each component for forming flocculation aid is uniformly mixed, then composition is adjusted
The each component of agent is matched after mixing by mass fraction, and composition mixture B is mixed evenly with flocculation aid;
Step 3: being matched by respective mass fraction, each component for forming flocculant is uniformly mixed composition mixture C;
Step 4: prepared mixture A is added in proportion into sludge to be conditioned, is carried out uniform stirring 1-3 hours;
Step 5: after mixing evenly, mixture B is added into sludge in proportion, is carried out uniform stirring 60-90 seconds, then to
Mixture C is wherein added, after uniform stirring 90-100 seconds, stands 5-10 minutes, filter-press dehydration, obtained moisture percentage in sewage sludge is
60% or less.
The mixing speed of the uniform stirring is 35-45 revs/min.
The dosage of the mixture A is the 0.3-0.6% of over dry mud (mud dry weight i.e. to be conditioned) quality to be conditioned;
The dosage of the mixture B is the 8-12% of over dry shale amount to be conditioned;The dosage of the mixture C is to be conditioned
The 0.1-0.2% of over dry shale amount.
Sludge conditioner of the present invention can carry out deep dehydration processing to sludge, and flocculation settling velocity is fast, effect is good, and dosage is not
Higher than sludge butt 10%, TDS amplification is lower than 60% less than 10%, moisture content of the cake, alternative traditional handicraft CaO and FeCl3
Combination, and preparation is simple, at low cost, it is without secondary pollution, it is de- to can be widely applied to the sludge such as all types of industries and life
Water drying and other treatment, treated, and sludge can be directly used for compost, agricultural soil, flower planting according to different regions actual features
Etc. a variety of disposal options, with good application prospect with market prospects.
Compared with prior art, the beneficial effects of the present invention are: sludge conditioners of the present invention to carry out depth to sludge
Dehydration, flocculation settling velocity is fast, effect is good, and preparation is simple, at low cost, without secondary pollution, has preferable
Application prospect and market prospects, sufficiently realize the minimizing of Treatment of Sludge, innoxious and resource utilization, and environmental protection is without dirt
Dye, function admirable is efficient, has preferable economic benefit and social benefit.It is described in detail below:
1, under the synergistic effect of each component, the microstate of sludge components, sludge conditioner and sludge can quickly be changed
Particle quickly forms firm wadding body, is conducive to the reduction of sludge specific resistance, and makes the freedom together with sludge Molecular Adsorption originally
Water base group's release, allows the invention to reach dehydrating effect significant compared with the prior art and dehydration efficiency.
2, the larger molecular organics of organic sludge can be degraded to small organic molecule by selected complex enzyme, make sludge
Clasmatosis discharges larger molecular organics intracellular, viscous to dissolve suspended solid and volatile suspended solids reduction sludge in sludge
Degree is to improve its dewatering and the friendly to environment.
3, sludge conditioner prepared by the present invention can carry out deep dehydration processing to sludge, and flocculation settling velocity is fast, effect
Good, water clarity is high out and effluent quality is excellent, and preparation is simple, at low cost, without secondary pollution, sufficiently realizes
The minimizing of Treatment of Sludge, innoxious and resource utilization, with good application prospect with market prospects.
Specific embodiment
The technical characteristic above-mentioned and other to the present invention is described in more detail with advantage below.
Embodiment 1:
A kind of sludge conditioner that can be widely applied in the Treatment of Sludge such as all types of industries waste water and sanitary sewage, including with
The raw material of lower mass fraction: 30 parts of porous adsorption carrier, 20 parts of biological enzyme material, 25 parts of flocculation aid, 15 parts of regulator, flocculant
15 parts.
Wherein porous adsorption carrier is made of zeolite powder, flyash, the short fine, maize cob meal of stalk and sepiolite powder mixing,
And each component takes 6 parts;Biological enzyme material is made of cellulase, protease, lysozyme, amylase mixing, and each component is equal
Take 5 parts;Flocculant is made of cationic modified starch, cationic polyacrylamide, sodium carboxymethylcellulose mixing, and each component
Mass fraction is respectively 5 parts, 6 parts, 4 parts;Regulator is made of sodium carbonate and sodium bicarbonate, and each component mass fraction is respectively
8 parts, 7 parts.
Embodiment 2:
A kind of sludge conditioner that can be widely applied in the Treatment of Sludge such as all types of industries waste water and sanitary sewage, including with
The raw material of lower mass fraction: 40 parts of porous adsorption carrier, 20 parts of biological enzyme material, 25 parts of flocculation aid, 15 parts of regulator, flocculant
15 parts.
Wherein porous adsorption carrier is made of zeolite powder, flyash, the short fine, maize cob meal of stalk and sepiolite powder mixing,
And each component takes 8 parts;Biological enzyme material is made of cellulase, protease, lysozyme, amylase mixing, and each component is equal
Take 5 parts;Flocculant is made of cationic modified starch, cationic polyacrylamide, sodium carboxymethylcellulose mixing, and each component
Mass fraction is respectively 5 parts, 6 parts, 4 parts;Regulator is made of sodium carbonate and sodium bicarbonate, and each component mass fraction is respectively
7.5 parts, 7.5 parts.
Embodiment 3:
A kind of sludge conditioner that can be widely applied in the Treatment of Sludge such as all types of industries waste water and sanitary sewage, including with
The raw material of lower mass fraction: 35 parts of porous adsorption carrier, 24 parts of biological enzyme material, 25 parts of flocculation aid, 15 parts of regulator, flocculant
15 parts.
Wherein porous adsorption carrier is made of zeolite powder, flyash, the short fine, maize cob meal of stalk and sepiolite powder mixing,
And each component takes 7 parts;Biological enzyme material is made of cellulase, protease, lysozyme, amylase mixing, and each component is equal
Take 6 parts;Flocculant is made of cationic modified starch, cationic polyacrylamide, sodium carboxymethylcellulose mixing, and each component
Mass fraction is respectively 5 parts, 6 parts, 4 parts;Regulator is made of sodium carbonate and sodium bicarbonate, and each component mass fraction is respectively
8 parts, 7 parts.
Embodiment 4:
A kind of sludge conditioner that can be widely applied in the Treatment of Sludge such as all types of industries waste water and sanitary sewage, including with
The raw material of lower mass fraction: 35 parts of porous adsorption carrier, 20 parts of biological enzyme material, 25 parts of flocculation aid, 6 parts of regulator, flocculant
15 parts.
Wherein porous adsorption carrier is made of zeolite powder, flyash, the short fine, maize cob meal of stalk and sepiolite powder mixing,
And each component takes 7 parts;Biological enzyme material is made of cellulase, protease, lysozyme, amylase mixing, and each component is equal
Take 5 parts;Flocculant is made of cationic modified starch, cationic polyacrylamide, sodium carboxymethylcellulose mixing, and each component
Mass fraction is respectively 5 parts, 6 parts, 4 parts;Regulator is sodium carbonate.
Embodiment 5:
The application method of sludge conditioner of the present invention is as follows:
Step 1: each component for forming porous adsorption carrier being matched by mass fraction and is uniformly mixed, then biological enzyme will be formed
The each component of material is matched after mixing by mass fraction, and composition mixture A is mixed evenly with porous adsorption carrier;
Step 2: being matched by respective mass fraction, each component for forming flocculation aid is uniformly mixed, then composition is adjusted
The each component of agent is matched after mixing by mass fraction, and composition mixture B is mixed evenly with flocculation aid;
Step 3: being matched by respective mass fraction, each component for forming flocculant is uniformly mixed composition mixture C;
Step 4: prepared mixture A is added in the ratio of over dry shale amount 0.5% to be conditioned to dirt to be conditioned
It in mud, carries out uniform stirring 1-3 hours, and mixing speed is 40 revs/min;
Step 5: after mixing evenly, mixture B is added in the ratio of over dry shale amount 10% to be conditioned into sludge,
It carries out uniform stirring 90 seconds and mixing speed is 40 revs/min, then press the ratio of over dry shale amount 0.15% to be conditioned thereto
Example adds mixture C, after uniform stirring 100 seconds and mixing speed are 40 revs/min, stands 10 minutes, filter-press dehydration.
By embodiment 1, embodiment 2, embodiment 3, embodiment 4 by the application method of embodiment 5 to sludge to be conditioned (wait adjust
Manage moisture percentage in sewage sludge 97%, pressure filtration yielding water transparency 225mm, out COD, NH of supernatant3- N, TP value are respectively 321.3mg/
L, 65.93mg/L, 36.79mg/L) it is improved, and detect its filters pressing moisture percentage in sewage sludge, pressure filtration yielding water transparency and water outlet
COD, NH of supernatant3- N, TP value, result data are as shown in the table:
Detection project | Embodiment 1 | Embodiment 2 | Embodiment 3 | Embodiment 4 |
Moisture content (%) | 56.32 | 57.29 | 56.59 | 58.12 |
Pressure filtration yielding water transparency (mm) | 752 | 748 | 746 | 742 |
pH | 7.68 | 7.84 | 7.91 | 7.73 |
COD degradation rate (%) | 94.38 | 91.08 | 90.89 | 90.12 |
Ammonia nitrogen degradation rate (%) | 89.59 | 86.49 | 85.13 | 86.78 |
TP degradation rate (%) | 95.12 | 94.07 | 91.56 | 93.45 |
It can be learnt as the result of upper table and improve conditioning as made from embodiment 1, embodiment 2, embodiment 3 and embodiment 4
Agent effectively can carry out deep dehydration processing to municipal wastewater treatment plant and trade effluent factory sludge, wherein obtained by embodiment 1
Conditioning conditioner compared with sludge conditioner is made in other embodiments effect it is more preferable, so sludge conditioning made from embodiment 1
Agent is highly preferred embodiment of the present invention.
The foregoing is only a preferred embodiment of the present invention, but scope of protection of the present invention is not limited thereto,
Anyone skilled in the art in the technical scope disclosed by the present invention, according to the technique and scheme of the present invention and its
Inventive concept is subject to equivalent substitution or change, should be covered by the protection scope of the present invention.
Claims (10)
1. a kind of sludge conditioner, it is characterised in that by mass fraction include following component:
30-40 parts of porous adsorption carrier, 20-25 parts of biological enzyme material, 25-30 parts of flocculation aid, 10-15 parts of regulator, flocculant
10-15 parts.
2. sludge conditioner according to claim 1, it is characterised in that:
30 parts of porous adsorption carrier, 20 parts of biological enzyme material, 25 parts of flocculation aid, 15 parts of regulator, 15 parts of flocculant.
3. sludge conditioner according to claim 1 or 2, it is characterised in that:
The porous adsorption carrier is by zeolite powder, flyash, the short fibre of stalk, maize cob meal, diatomite, attapulgite, sepiolite
At least three kinds mixing composition in powder, and each component quality is impartial.
4. sludge conditioner according to claim 1 or 2, it is characterised in that:
The biological enzyme material is by cellulase, protease, pectase, catalase, lysozyme, amylase, lipase
At least three kinds mixing composition, and each component quality is impartial.
5. sludge conditioner according to claim 1 or 2, it is characterised in that:
The flocculation aid is made of magnesium salts and silicate, and each component quality is 1:1.
6. sludge conditioner according to claim 5, it is characterised in that:
The magnesium salts is made of the mixing of the ratio of magnesia and magnesium sulfate 0.5:1.5 in mass ratio;The silicate by alumina silicate,
Calcium silicates and sodium metasilicate 1:1:1 in mass ratio mixing are constituted.
7. sludge conditioner according to claim 1 or 2, it is characterised in that:
The regulator includes sodium carbonate and/or sodium bicarbonate.
8. sludge conditioner according to claim 1 or 2, it is characterised in that:
The flocculant is cationic modified starch, cationic polyacrylamide, sodium carboxymethylcellulose, two allyl of poly dimethyl
At least one of ammonium chloride, polyethyleneimine.
9. a kind of application method of sludge conditioner of any of claims 1 or 2, it is characterised in that include the following steps:
Step 1: each component for forming porous adsorption carrier being matched by mass fraction and is uniformly mixed, then biological enzyme material will be formed
Each component by mass fraction match after mixing, composition mixture A is mixed evenly with porous adsorption carrier;
Step 2: matching, each component for forming flocculation aid is uniformly mixed, then regulator will be formed by respective mass fraction
Each component is matched after mixing by mass fraction, and composition mixture B is mixed evenly with flocculation aid;
Step 3: being matched by respective mass fraction, each component for forming flocculant is uniformly mixed composition mixture C;
Step 4: prepared mixture A is added in proportion into sludge to be conditioned, is carried out uniform stirring 1-3 hours;
Step 5: after mixing evenly, mixture B being added into sludge in proportion, carried out uniform stirring 60-90 seconds, then thereto
Mixture C is added, after uniform stirring 90-100 seconds, stands 5-10 minutes, filter-press dehydration.
10. application method according to claim 9, it is characterised in that:
The dosage of the mixture A is the 0.3-0.6% of over dry shale amount to be conditioned;The dosage of the mixture B is
The 8-12% of over dry shale amount to be conditioned;The dosage of the mixture C is the 0.1- of over dry shale amount to be conditioned
0.2%.
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CN201910705666.XA CN110372174A (en) | 2019-08-01 | 2019-08-01 | A kind of sludge conditioner and its application |
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Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
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CN111018283A (en) * | 2019-12-13 | 2020-04-17 | 中交(天津)生态环保设计研究院有限公司 | Plate-frame filter-pressing dehydration method for river and lake bottom mud |
CN111018282A (en) * | 2019-12-12 | 2020-04-17 | 中交(天津)生态环保设计研究院有限公司 | Porous biological polymerization agent for dewatering ecological dredging bottom mud of rivers and lakes |
CN111995222A (en) * | 2020-09-24 | 2020-11-27 | 神美科技有限公司 | Sludge conditioner |
CN112174492A (en) * | 2020-09-30 | 2021-01-05 | 神美科技有限公司 | Composite sludge conditioner |
CN112374710A (en) * | 2020-11-20 | 2021-02-19 | 广州市凯卫莎环保科技有限公司 | Sludge dewatering and drying process technology and dewatering and drying system |
CN112745009A (en) * | 2020-08-29 | 2021-05-04 | 杭州国泰环保科技股份有限公司 | Sludge conditioning agent suitable for different mud characteristics and treatment process |
CN114031266A (en) * | 2021-11-05 | 2022-02-11 | 苏州埃斯腾特生物科技有限公司 | Leachate sludge dewatering composite biological enzyme conditioner and preparation and use methods thereof |
CN114702229A (en) * | 2022-03-16 | 2022-07-05 | 广州诺冠环保科技有限公司 | Compound municipal sludge improvement agent and preparation method and application thereof |
CN114772974A (en) * | 2022-03-28 | 2022-07-22 | 安徽华仕纳米科技有限公司 | Concrete residual material nano regeneration treatment agent, preparation method and application thereof |
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Cited By (13)
Publication number | Priority date | Publication date | Assignee | Title |
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CN111018282A (en) * | 2019-12-12 | 2020-04-17 | 中交(天津)生态环保设计研究院有限公司 | Porous biological polymerization agent for dewatering ecological dredging bottom mud of rivers and lakes |
CN111018282B (en) * | 2019-12-12 | 2020-11-24 | 中交(天津)生态环保设计研究院有限公司 | Porous biological polymerization agent for dewatering ecological dredging bottom mud of rivers and lakes |
US20220332621A1 (en) * | 2019-12-12 | 2022-10-20 | Cccc (Tianjin) Eco-Environmental Protection Design & Research Institute Co., Ltd. | Porous biological polymerizing agent for sediment dewatering in environmental dredging of rivers and lakes |
WO2021114997A1 (en) * | 2019-12-12 | 2021-06-17 | 中交(天津)生态环保设计研究院有限公司 | Porous biological polymerizer for river and lake ecological dredging and dewatering of sediment |
CN111018283A (en) * | 2019-12-13 | 2020-04-17 | 中交(天津)生态环保设计研究院有限公司 | Plate-frame filter-pressing dehydration method for river and lake bottom mud |
CN112745009A (en) * | 2020-08-29 | 2021-05-04 | 杭州国泰环保科技股份有限公司 | Sludge conditioning agent suitable for different mud characteristics and treatment process |
CN111995222A (en) * | 2020-09-24 | 2020-11-27 | 神美科技有限公司 | Sludge conditioner |
CN112174492A (en) * | 2020-09-30 | 2021-01-05 | 神美科技有限公司 | Composite sludge conditioner |
CN112374710A (en) * | 2020-11-20 | 2021-02-19 | 广州市凯卫莎环保科技有限公司 | Sludge dewatering and drying process technology and dewatering and drying system |
CN114031266A (en) * | 2021-11-05 | 2022-02-11 | 苏州埃斯腾特生物科技有限公司 | Leachate sludge dewatering composite biological enzyme conditioner and preparation and use methods thereof |
CN114702229A (en) * | 2022-03-16 | 2022-07-05 | 广州诺冠环保科技有限公司 | Compound municipal sludge improvement agent and preparation method and application thereof |
CN114702229B (en) * | 2022-03-16 | 2024-01-26 | 广州诺冠环保科技有限公司 | Composite municipal sludge improvement medicament and preparation method and application thereof |
CN114772974A (en) * | 2022-03-28 | 2022-07-22 | 安徽华仕纳米科技有限公司 | Concrete residual material nano regeneration treatment agent, preparation method and application thereof |
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Application publication date: 20191025 |