CN108892358A - A kind of high-efficiency composite biological flocculant and preparation method thereof for Treatment of Sludge - Google Patents

A kind of high-efficiency composite biological flocculant and preparation method thereof for Treatment of Sludge Download PDF

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Publication number
CN108892358A
CN108892358A CN201811058884.0A CN201811058884A CN108892358A CN 108892358 A CN108892358 A CN 108892358A CN 201811058884 A CN201811058884 A CN 201811058884A CN 108892358 A CN108892358 A CN 108892358A
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China
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sludge
treatment
parts
biological flocculant
composite biological
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CN201811058884.0A
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Chinese (zh)
Inventor
张琪
张学瑞
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Qingdao Boryou Biotechnology Co Ltd
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Qingdao Boryou Biotechnology Co Ltd
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Priority to CN201811058884.0A priority Critical patent/CN108892358A/en
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/14Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents

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

Abstract

The high-efficiency composite biological flocculant and preparation method thereof that the invention discloses a kind of for Treatment of Sludge.The high-efficiency composite biological flocculant for Treatment of Sludge includes according to mass fraction:10~70 parts of polymeric amino acid, 10~50 parts of animal gelatin, 0.1~20 part of uronic acid and sulfate composite chlorate PBT0.1~10 part.Flocculant of the invention is a kind of simultaneously containing organic and inorganic macromolecule compound reticular structure mixture, effect is swept by charging neutrality, absorption, bridge formation and volume and water-borne glue body particle forms close uniform wadding body, it is good with product stability, dosage is small, the features such as flocculating effect is good, and treatment effeciency is high, and sludge yield is small, it is more environmentally-friendly compared to polyacrylamide, it is widely portable to the processing of sewage, waste water.

Description

A kind of high-efficiency composite biological flocculant and preparation method thereof for Treatment of Sludge
Technical field
The present invention relates to sewage sludge process fields, and in particular to a kind of high-efficiency composite biological flocculation for Treatment of Sludge Agent and preparation method thereof.
Background technique
It is sharply increased with the rapid development of industry with population, cities and towns drink earth's surface water demand and industrial wastewater, city City's sanitary sewage, breeding wastewater discharge amount are growing day by day.Since sewage discharge type constantly rises, water pollutant ingredient becomes It becomes increasingly complex, therefore the difficulty handled sewage is also increasing.It, can be to industrial and agricultural production and people if dealt with improperly Class health is to seriously threatening.State lives the portion's of building notification and explicitly points out, and increases specific resistance to filtration working dynamics into next step work Make emphasis, target is to the year two thousand twenty bottom, and ground level and the above municipal sludge harmlessness disposing rate reach 90%, other cities reach 75%;Strive reaching 60% in county town.
More commonly used in industry at present is to carry out flocculation treatment to water-containing sludge using polyacrylamide (abbreviation PAM). But because mud, water can be coated togather simultaneously by its covering property, even if causing to be added to the auxiliary materials such as stalk during later stage fermentation And strain can not also make sludge really be fermented.Since sludge is under anaerobic state always, it is not suitable for depositing for bacterium It is living, so resulting in the mortality of strain;Longer drying cycle makes the organic matter transformation in sludge for ammonia, vulcanization The gases such as hydrogen, alkanes are largely lost, and the stench constantly issued has also seriously affected surrounding enviroment.
Biological flocculant refers to various functional protein, functional polysaccharose substance with flocculation activity, it micro- Seeing stereochemical structure mainly includes fibrous structure and chondritic, its flocculation mechanism mainly includes bridge linking effect, neutralization With the volume effect of sweeping.Effectively overcome that inorganic flocculating agent and artificial synthesized organic flocculant are existing in terms of safety and environment to ask Topic, is environmentally friendly green flocculant, the increasingly attention by various countries water treatment work person.
Summary of the invention
The high-efficiency composite biological flocculant and preparation method thereof that the purpose of the present invention is to provide a kind of for Treatment of Sludge, Existing compound biological flocculant (CBF) is modified by sulfate composite chlorate PBT, it is good again to obtain a kind of compressibility Novel flocculant with good flocculating effect.
To achieve the above object, the present invention provides a kind of high-efficiency composite biological flocculants for Treatment of Sludge.Specifically , the high-efficiency composite biological flocculant for Treatment of Sludge includes according to mass fraction:10~70 parts of polymeric amino acid, 10~50 parts of animal gelatin, 0.1~20 part of uronic acid and sulfate composite chlorate PBT0.1~10 part.
Preferably, the high-efficiency composite biological flocculant for Treatment of Sludge includes according to mass fraction:It polymerize ammonia 25~55 parts of base acid, 20~30 parts of animal gelatin, 5~12 parts of uronic acid and sulfate composite chlorate PBT2~6 part.
Preferably, the high-efficiency composite biological flocculant for Treatment of Sludge includes according to mass fraction:It polymerize ammonia 40 parts of base acid, 25 parts of animal gelatin, 8 parts of uronic acid and PBT4 parts of sulfate composite chlorate.
Preferably, the polymeric amino acid be one of glycine, alanine, leucine, lysine and serine or It is a variety of.
Preferably, the uronic acid is glucuronic acid, mannuronic acid, galacturonic acid, iduronic acid and Gu Luo One of uronic acid is a variety of.
Preferably, the sulfate composite chlorate PBT includes polyaluminum sulfate aluminium chloride (PACS) and polyaluminum sulfate aluminium chloride Iron (PAFCS).
Preferably, the mass ratio of the polyaluminum sulfate aluminium chloride (PACS) and polyaluminum sulfate aluminium chloride ferrum (PAFCS) are 5: 1。
Preferably, the high-efficiency composite biological flocculant is suitable for the water body that pH value is 3.0~11.0.
Second aspect of the present invention provides a kind of preparation method of high-efficiency composite biological flocculant for Treatment of Sludge.Tool Body, the preparation method includes the following steps:
(1) polymeric amino acid and aldehyde glycan are added to formalin, are slowly stirred 20~30min, are received after centrifuge separation Collect supernatant liquor;
(2) supernatant liquor is warming up to 40 DEG C, is slowly added to animal gelatin, under the conditions of 60~75 DEG C, with revolving speed 150~ 200rpm is stirred 2~3 hours;
(3) sulfate composite chlorate PBT is added, uniform stirring is cooled to room temperature to after being completely dissolved, and spontaneous nucleation obtains Flocculant crude product;
(4) crude product, using vacuum drying, obtains Compound biological flocculant after methanol washing purification.
The method of the present invention has the following advantages that:
High-efficiency composite biological flocculant for Treatment of Sludge of the invention is that one kind contains organic and inorganic high score simultaneously The reticular structure mixture of sub- compound passes through the effect of sweeping of charging neutrality, absorption, bridge formation and volume during flocculation sedimentation Close uniform wadding body is formed with water-borne glue body particle, thus stratification sedimentation, and then formed and stablize mud-water separation system.
In addition, product of the present invention has the characteristics that easy to operate, materials are convenient, compressibility is good, mud-water separation interface is clear, Water pollutant can be more removed, and preferably can firmly be lockked mud in the pressure-filtering process of sludge, sludge contains Water is lower than other flocculants, and the sewage after filters pressing is also relatively limpid, can preferably play the minimizing of sludge, can will be present The general polyacrylamide perfection of sewage treatment replaces, and pollution will not be generated to environment after use, to terminate Sewage The history that mud cannot degrade.
Specific embodiment
The following examples are used to illustrate the present invention, but are not intended to limit the scope of the present invention..
Embodiment 1
The preparation method of the high-efficiency composite biological flocculant for Treatment of Sludge of the present embodiment, prepares according to the following steps:
(1) by 10 parts of glycine, 10 parts of alanine, 10 parts of leucines, 10 parts of serines, 3 parts of glucuronic acids, 3 part half Lactobionic acid and 2 parts of iduronic acids are added to formalin, are slowly stirred 25min, collect supernatant liquor after centrifuge separation;
(2) supernatant liquor is warming up to 40 DEG C, is slowly added to 25 parts of animal gelatins, under the conditions of 70 DEG C, with revolving speed 180rpm Stirring 2.5 hours;
(3) 4 parts of sulfate composite chlorate PBT (polyaluminum sulfate aluminium chloride (PACS) and polyaluminum sulfate aluminium chloride ferrum is added (PAFCS) mass ratio=5:1), uniform stirring is cooled to room temperature to after being completely dissolved, and spontaneous nucleation obtains flocculant crude product;
(4) crude product, using vacuum drying, obtains Compound biological flocculant after methanol washing purification.
Embodiment 2
The preparation method of the high-efficiency composite biological flocculant for Treatment of Sludge of the present embodiment, prepares according to the following steps:
(1) 4 parts of leucines, 4 parts of lysines, 2 parts of serines, 2.5 parts of iduronic acids and 2.5 parts of guluronic acids are added Enter to formalin, is slowly stirred 20min, collects supernatant liquor after centrifuge separation;
(2) supernatant liquor is warming up to 40 DEG C, is slowly added to 50 parts of animal gelatins, under the conditions of 60 DEG C, with revolving speed 160rpm Stirring 2 hours;
(3) 6 parts of sulfate composite chlorate PBT (polyaluminum sulfate aluminium chloride (PACS) and polyaluminum sulfate aluminium chloride ferrums are added (PAFCS) mass ratio is 5:1), uniform stirring is cooled to room temperature to after being completely dissolved, and spontaneous nucleation obtains flocculant crude product;
(4) crude product, using vacuum drying, obtains Compound biological flocculant after methanol washing purification.
Embodiment 3
(1) 15 parts of leucines, 15 parts of lysines, 25 parts of serines and 0.1 part of galacturonic acid are added to formalin, It is slowly stirred 30min, collects supernatant liquor after centrifuge separation;
(2) supernatant liquor is warming up to 40 DEG C, is slowly added to 30 parts of animal gelatins, under the conditions of 65 DEG C, with revolving speed 150rpm Stirring 3 hours;
(3) 2 parts of sulfate composite chlorate PBT (polyaluminum sulfate aluminium chloride (PACS) and polyaluminum sulfate aluminium chloride ferrums are added (PAFCS) mass ratio is 5:1), uniform stirring is cooled to room temperature to after being completely dissolved, and spontaneous nucleation obtains flocculant crude product;
(4) crude product, using vacuum drying, obtains Compound biological flocculant after methanol washing purification.
Embodiment 4
The preparation method of the high-efficiency composite biological flocculant for Treatment of Sludge of the present embodiment, prepares according to the following steps:
(1) that 40 parts of leucines, 30 parts of lysines, 6 parts of glucuronic acids and 6 parts of guluronic acids are added to formaldehyde is molten Liquid is slowly stirred 20~30min, collects supernatant liquor after centrifuge separation;
(2) supernatant liquor is warming up to 40 DEG C, is slowly added to 10 parts of animal gelatins, under the conditions of 75 DEG C, with revolving speed 200rpm Stirring 3 hours;
(3) 10 parts of sulfate composite chlorate PBT (polyaluminum sulfate aluminium chloride (PACS) and polyaluminum sulfate aluminium chloride ferrums are added (PAFCS) mass ratio is 5:1), uniform stirring is cooled to room temperature to after being completely dissolved, and spontaneous nucleation obtains flocculant crude product;
(4) crude product, using vacuum drying, obtains Compound biological flocculant after methanol washing purification.
Embodiment 5
The preparation method of the high-efficiency composite biological flocculant for Treatment of Sludge of the present embodiment, prepares according to the following steps:
(1) that 10 parts of leucines, 15 parts of serines, 5 parts of mannuronic acids and 15 parts of galacturonic acids are added to formaldehyde is molten Liquid is slowly stirred 20~30min, collects supernatant liquor after centrifuge separation;
(2) supernatant liquor is warming up to 40 DEG C, is slowly added to 20 parts of animal gelatins, under the conditions of 68 DEG C, with revolving speed 190rpm Stirring 2 hours;
(3) 10 parts of sulfate composite chlorate PBT (polyaluminum sulfate aluminium chloride (PACS) and polyaluminum sulfate aluminium chloride ferrums are added (PAFCS) mass ratio is 5:1), uniform stirring is cooled to room temperature to after being completely dissolved, and spontaneous nucleation obtains flocculant crude product;
(4) crude product, using vacuum drying, obtains Compound biological flocculant after methanol washing purification.
The flocculation turbidity removal effect of sewage is verified:
Flocculating rate (%)=(A-B)/A × 100
In formula, the absorbance value of A- blank water sample supernatant, the absorbance value of B- water sample supernatant to be measured.
Table 1 is the high-efficiency composite biological flocculant sewage flocculation for Treatment of Sludge of Examples 1 to 5 preparation
Rate test result
From table 1 it follows that the high-efficiency composite biological for Treatment of Sludge prepared by the embodiment of the present invention 1~5 is wadded a quilt with cotton Solidifying agent is suitable for the water body that pH value is 3.0~11.0, and flocculating rate average 95% or so has dosage small, and flocculating effect is good, processing It is high-efficient, the features such as sludge yield is small.
Although above having used general explanation and specific embodiment, the present invention is described in detail, at this On the basis of invention, it can be made some modifications or improvements, this will be apparent to those skilled in the art.Therefore, These modifications or improvements without departing from theon the basis of the spirit of the present invention are fallen within the scope of the claimed invention.

Claims (9)

1. a kind of high-efficiency composite biological flocculant for Treatment of Sludge, it is characterised in that:The height for Treatment of Sludge Compound biological flocculant, which is imitated, according to mass fraction includes:10~70 parts of polymeric amino acid, 10~50 parts of animal gelatin, uronic acid 0.1~20 part and sulfate composite chlorate PBT0.1~10 part.
2. the high-efficiency composite biological flocculant according to claim 1 for Treatment of Sludge, it is characterised in that:The use Include according to mass fraction in the high-efficiency composite biological flocculant of Treatment of Sludge:25~55 parts of polymeric amino acid, animal gelatin 20 ~30 parts, 5~12 parts of uronic acid and sulfate composite chlorate PBT2~6 part.
3. the high-efficiency composite biological flocculant according to claim 2 for Treatment of Sludge, it is characterised in that:The use Include according to mass fraction in the high-efficiency composite biological flocculant of Treatment of Sludge:40 parts of polymeric amino acid, 25 parts of animal gelatin, sugar 4 parts of 8 parts of aldehydic acid and sulfate composite chlorate PBT.
4. the high-efficiency composite biological flocculant according to claim 1-3 for Treatment of Sludge, it is characterised in that: The polymeric amino acid is one of glycine, alanine, leucine, lysine and serine or a variety of.
5. the high-efficiency composite biological flocculant according to claim 1-3 for Treatment of Sludge, it is characterised in that: The uronic acid be one of glucuronic acid, mannuronic acid, galacturonic acid, iduronic acid and guluronic acid or It is a variety of.
6. the high-efficiency composite biological flocculant according to claim 1-3 for Treatment of Sludge, it is characterised in that: The sulfate composite chlorate PBT includes polyaluminum sulfate aluminium chloride (PACS) and polyaluminum sulfate aluminium chloride ferrum (PAFCS).
7. the high-efficiency composite biological flocculant according to claim 6 for Treatment of Sludge, it is characterised in that:The polymerization The mass ratio of aluminum chloride sulphate (PACS) and polyaluminum sulfate aluminium chloride ferrum (PAFCS) are 5:1.
8. the high-efficiency composite biological flocculant according to claim 1 for Treatment of Sludge, it is characterised in that:It is described efficient Compound biological flocculant is suitable for the water body that pH value is 3.0~11.0.
9. a kind of preparation method for the high-efficiency composite biological flocculant of Treatment of Sludge as described in claim 1, feature It is:The preparation method includes the following steps:
(1) polymeric amino acid and aldehyde glycan are added to formalin, are slowly stirred 20~30min, collected after centrifuge separation Layer clear liquid;
(2) supernatant liquor is warming up to 40 DEG C, is slowly added to animal gelatin, under the conditions of 60~75 DEG C, with 150~200rpm of revolving speed Stirring 2~3 hours;
(3) sulfate composite chlorate PBT is added, uniform stirring is cooled to room temperature to after being completely dissolved, and spontaneous nucleation is flocculated Agent crude product;
(4) crude product, using vacuum drying, obtains Compound biological flocculant after methanol washing purification.
CN201811058884.0A 2018-09-11 2018-09-11 A kind of high-efficiency composite biological flocculant and preparation method thereof for Treatment of Sludge Pending CN108892358A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113105541A (en) * 2021-04-23 2021-07-13 浙江崇山生物制品有限公司 Method for purifying collagen

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03161100A (en) * 1989-11-21 1991-07-11 Ebara Infilco Co Ltd Treatment process for sludge in purifying tank
CN101219828A (en) * 2008-01-24 2008-07-16 云南大学 Blue algae water bloom bioflocculation agent and production
CN101693561A (en) * 2009-10-13 2010-04-14 河海大学 Method for preparing compound flocculating agent
CN107265666A (en) * 2017-08-08 2017-10-20 苏州吉利不锈钢制品有限公司 A kind of stainless steel production wastewater biological flocculant and preparation method thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03161100A (en) * 1989-11-21 1991-07-11 Ebara Infilco Co Ltd Treatment process for sludge in purifying tank
CN101219828A (en) * 2008-01-24 2008-07-16 云南大学 Blue algae water bloom bioflocculation agent and production
CN101693561A (en) * 2009-10-13 2010-04-14 河海大学 Method for preparing compound flocculating agent
CN107265666A (en) * 2017-08-08 2017-10-20 苏州吉利不锈钢制品有限公司 A kind of stainless steel production wastewater biological flocculant and preparation method thereof

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
张泾生等: "《矿用药剂》", 30 November 2008, 冶金工业出版社 *
朱云等: "《冶金设备》", 30 September 2013, 冶金工业出版社 *
蔡德明等: "《教育研究论丛(第三辑)》", 31 May 2003, 武汉理工大学出版社 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113105541A (en) * 2021-04-23 2021-07-13 浙江崇山生物制品有限公司 Method for purifying collagen
CN113105541B (en) * 2021-04-23 2022-03-11 浙江崇山生物制品有限公司 Method for purifying collagen

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Application publication date: 20181127