CN104560939B - A kind of preparation method of bacteria carrier particle - Google Patents

A kind of preparation method of bacteria carrier particle Download PDF

Info

Publication number
CN104560939B
CN104560939B CN201410717114.8A CN201410717114A CN104560939B CN 104560939 B CN104560939 B CN 104560939B CN 201410717114 A CN201410717114 A CN 201410717114A CN 104560939 B CN104560939 B CN 104560939B
Authority
CN
China
Prior art keywords
bacterium
particle
core
bacteria
encapsulating layer
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.)
Expired - Fee Related
Application number
CN201410717114.8A
Other languages
Chinese (zh)
Other versions
CN104560939A (en
Inventor
范铮
张国亮
秦磊
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.)
Zhejiang University of Technology ZJUT
Original Assignee
Zhejiang University of Technology ZJUT
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 Zhejiang University of Technology ZJUT filed Critical Zhejiang University of Technology ZJUT
Priority to CN201410717114.8A priority Critical patent/CN104560939B/en
Publication of CN104560939A publication Critical patent/CN104560939A/en
Application granted granted Critical
Publication of CN104560939B publication Critical patent/CN104560939B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Immobilizing And Processing Of Enzymes And Microorganisms (AREA)

Abstract

The invention discloses a kind of preparation method of bacteria carrier particle, including:Step 1:Make core A:Core A is the coccoid particle being prepared by mixing into by filler, expanding agent and adhesive, is then dried;Step 2:In core A external applications oxireme, oxirane or polyvinyl chloride as sealant B, turn into an enclosed interior and contain cuniculate bead;Step 3:In suitable culture medium, bacterium is cultivated by progressively amplification, to the 5th generation, is concentrated with high speed centrifugation, controls 0~4 DEG C of temperature, mixed with encapsulating layer C;Step 4:The encapsulating layer C of mixing is coated in bead surface, forms the outer layer of bacterium embedded particles;Step 5:Under 0~4 DEG C of temperature conditions, the particle is squeezed into CaCl2The immobilization particle of crosslinking shaping about 4~6mm diameters in solution.The beneficial effects of the invention are as follows:It is easy to cultivate bacterium in wastewater disposal basin, particle is capable of the bacterium of high capacity.

Description

A kind of preparation method of bacteria carrier particle
Technical field
The invention belongs to the preparation method of carrier granular, is related to a kind of preparation method of bacteria carrier particle.
Background technology
Immobilization technology refers to enzyme immobilizatio and the immobilization technology of bacterium.Since the seventies in last century, people are first First exploitation has used enzyme immobilization technology, and the immobilization technology of bacterium is grown up on the basis of enzyme immobilization technology 's.Immobilization bacterium technology is exactly using chemically or physically Method means, by the bacteria adhension of common free state in a certain limit Fixed space, with and improve the concentration of bacterium, and take certain method bacterium is kept higher activity, extend using period, It can accomplish to recycle.Research and application show:By immobilization bacterium technology bacterial density raising, biochemical process can be made anti- Speed is answered to accelerate, the resistance to murder by poisoning ability of bacterium is strong, bacterium is lost in less during successive reaction or continuous degradation, raw material and product divide The advantages that being minimized from easy, stable, reaction unit.At present, immobilization bacterium technology is to good performance, extensively The general research applied in terms of environmental pollution improvement, main object of administering is intractable organic wastewater and heavy metal pollution Waste water, while achievement is related to the pollution control of air and soil.
Although bacteria adhension has above advantage, there is also light diffusion, light transmission, substrate and product in reaction solution Diffusion mass transfer is difficult, the problems such as immobilization particle easy dispersing and dissolving.At present, surface particles are all integration, whole grain.This Patent devises a kind of embedded particles new technology first, and embedded particles are divided into the core layer of centre and outside encapsulating layer.By It is poor in existing particle internal mass transfer, transmitted light is not easy, has extraneous (solution) to be not easy to carry out mass exchange, and bacterium inside particle It is difficult to enter, bacterial growth is few, therefore inner sealing is got up, and is configured as the skeleton of particle, plays floating and fixation;Outside Layer can fully receive light, facilitate conveying between mass transfer and material.So it is bacterial growth layer, degradation by exterior design Layer, is embedded in outer layer by bacterium, porosity and channel diameter can be easily increased in outer layer.Solve light diffusion and substrate with this And product diffusion mass transfer is difficult.Improve the validity of the degraded of embedded particles and improve the influence of glucose substrate degradation characteristic.
The content of the invention
It is an object of the present invention to overcome the deficiencies in the prior art, there is provided one kind is easy to Bacteria Culture, is run in MBR Cheng Zhongke improve degradation speed, reduce sludge quantity bacteria carrier particle preparation method.
The preparation method of the bacteria carrier particle of the present invention, including:
Step 1:Make core A:Core A is the coccoid particle being prepared by mixing into by filler, expanding agent and adhesive, its Ratio is 50~80%, 10%~25%, 10~25%;2~3mm diameters, are then dried, and ensure the hardness of particle and certain Elasticity, internally there is certain space;The filler is diatomite, polyamide or activated carbon;The expanding agent is ammonium carbonate;Institute It is addition polymerization ethylene glycol, polyvinyl alcohol or oxirane to state adhesive;
Step 2:In core A external applications oxireme, oxirane or polyvinyl chloride as sealant B, turn into one Enclosed interior contains cuniculate bead;
Step 3:In suitable culture medium, bacterium is cultivated by progressively amplification, it is dense with high speed centrifugation to the 5th generation Contracting, 0~4 DEG C of temperature is controlled, mixed with encapsulating layer C;The encapsulating layer C is by sodium alginate, polyethylene glycol, polyvinyl alcohol system , its ratio is 70%~90%, 5%~15%, 5%~15%, has stronger cohesive to have preferable elasticity, and can be useless Bacterium is protected in water, is progressively sustained bacterium;
Step 4:The encapsulating layer C of mixing is coated in bead surface, forms the outer layer of bacterium embedded particles;
Step 5:Under 0~4 DEG C of temperature conditions, the particle is squeezed into CaCl2Crosslinking shaping 4~6mm diameters in solution Immobilization particle.
As preferred:The bacterium of embedding is actinomyces, photosynthetic bacteria, Degrading genetical engineering of microorganism or production compound bacteria.
The beneficial effects of the invention are as follows:
1st, the bacteria carrier particle of the invention as made from a kind of bacteria adhension technology, it is thin to be easy to culture in wastewater disposal basin Bacterium, the particle can reach efficient, impact-resistant effect, simultaneously because the containing of sodium alginate, polyethylene glycol, polyvinyl alcohol Property so that particle is capable of the bacterium of high capacity.
2nd, the particle is easy to use in common biochemical reaction tank, can also be coupled with membrane bioreactor.
3rd, it is not easily broken, especially internal core has tunic protection so that it is internal intact all the time, while can protect Grain has floatability.
4th, the cavity size of internal core, how much can be adjusted by the quantity of ammonium carbonate, control, realize regulation particle Proportion, it is possible thereby to position of the embedded particles in water be adjusted, such as at waste liquid pool bottom or top, or in centre floating.
5th, carrier granular of the invention can load 1:1~l:5 ratio embedding bacterium (bacterial weight:Embedding medium weight Amount).The particle squeezes into CaCl under 0~4 DEG C of temperature conditions, by little particle2, be crosslinked in the solution such as glutaraldehyde, being fixed Particle.
Brief description of the drawings
Fig. 1 is schematic diagram of the present invention;
Embodiment
The present invention is described further with reference to the accompanying drawings and examples.Although the present invention will enter with reference to preferred embodiment Row description, it should be understood that being not offered as limiting the invention in the embodiment.It can be included on the contrary, the present invention will cover Alternative, modified and the equivalent in the scope of the present invention that appended claims limits.
As shown in figure 1, the preparation method of the bacteria carrier particle of the present invention:Grain skeleton is formed by diatomite, with carbonic acid Ammonium is expanding agent, prepares to form 20~30mm granular cores using polyethylene glycol as adhesive, diatomite, polyethylene glycol, ammonium carbonate The ratio between be 7:2:1, the thick embryo of the core through drying, 80 DEG C roasting etc. handling process, inside be to have certain cavity.Use oxirane As sealant.By the use of sodium alginate, polyethylene glycol, polyvinyl alcohol as encapsulating layer embed bacterium, sodium alginate, polyethylene glycol, The ratio between polyvinyl alcohol is 5:2:1,40~60mm immobilization particle is formed, particle can freely move in water made from the technology It is dynamic.The activity and impact resistance of bacterium can be improved.There are some successful cases using bacteria adhension technology:
Case study on implementation 1
It is 3000mg/L, COD 1500mg/ in dyeing waste water BOD using a certain amount of carrier granular as made from the technology In L solution, carrier granular injected volume is 1~2.5%, under aerobic condition, is degraded through 3 days, BOD have dropped 81.5%, COD It has dropped 83.0%.
Case study on implementation 2
It is the molasses that 5000mg/L, COD are 1800mg/L in BOD using a certain amount of carrier granular as made from the technology In waste water, carrier granular injected volume is 0.5~1.5%, under aerobic condition, is degraded through 3 days, BOD have dropped 90.5%, COD It has dropped 93.6%.
Case study on implementation 3
It is the soya-bean milk that 5500mg/L, COD are 2200mg/L in BOD using a certain amount of carrier granular as made from the technology In waste water, carrier granular injected volume is 0.5~5%, under aerobic condition, is degraded through 3 days, BOD have dropped under 95.5%, COD Drop 92.3%.
Case study on implementation 4
It is the life that 2500mg/L, COD are 2400mg/L in BOD using a certain amount of carrier granular as made from the technology In waste water, carrier granular injected volume is 1~3.4%, under anaerobic, is degraded through 3 days, under aerobic condition, is dropped through 2 days Solution, BOD have dropped 94.5%, COD and have dropped 94.6%.
Case study on implementation 5
It is the rubbish that 8500mg/L, COD are 5500mg/L in BOD using a certain amount of carrier granular as made from the technology Effusion, carrier granular injected volume is 0.5~2.5%, under anaerobism, aerobic condition, is respectively degraded through 5 days, BOD have dropped 85.5%th, COD have dropped 79.1%.
Case study on implementation 6
It is the pharmacy that 3500mg/L, COD are 1800mg/L in BOD using a certain amount of carrier granular as made from the technology In waste water, ammonia nitrogen waste water 180mg/L, carrier granular injected volume is 1~3.5%, under anaerobism, aerobic condition, is respectively dropped through 5 days Solution, BOD have dropped 90.6%, COD and have dropped 81.8%, and ammonia nitrogen declines 86.1%.

Claims (2)

  1. A kind of 1. preparation method of bacteria carrier particle, it is characterised in that including:
    Step 1:Make core A:Core A is the coccoid particle being prepared by mixing into by filler, expanding agent and adhesive, its ratio For 50~80%, 10%~25%, 10~25%;2~3mm diameters, are then dried, and ensure the hardness of particle and certain bullet Property, internally there is certain space;The filler is diatomite, polyamide or activated carbon;The expanding agent is ammonium carbonate;It is described Adhesive is addition polymerization ethylene glycol, polyvinyl alcohol or oxirane;
    Step 2:In core A external applications oxireme, oxirane or polyvinyl chloride as sealant B, turn into one it is closed Inside contains cuniculate bead;
    Step 3:In suitable culture medium, bacterium is cultivated by progressively amplification, to the 5th generation, is concentrated, controlled with high speed centrifugation 0~4 DEG C of temperature processed, mixed with encapsulating layer C;The encapsulating layer C is made by sodium alginate, polyethylene glycol, polyvinyl alcohol, its Ratio is 70%~90%, 5%~15%, 5%~15%, has stronger cohesive to have preferable elasticity, and can be in waste water Bacterium is protected, is progressively sustained bacterium;
    Step 4:The encapsulating layer C of mixing is coated in bead surface, forms the outer layer of bacterium embedded particles;
    Step 5:Under 0~4 DEG C of temperature conditions, the particle is squeezed into CaCl2The immobilization of crosslinking shaping 4~6mm diameters in solution Particle.
  2. 2. the preparation method of bacteria carrier particle according to claim 1, it is characterised in that:The bacterium of embedding is unwrapping wire Bacterium, photosynthetic bacteria, Degrading genetical engineering of microorganism or production compound bacteria.
CN201410717114.8A 2014-12-01 2014-12-01 A kind of preparation method of bacteria carrier particle Expired - Fee Related CN104560939B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410717114.8A CN104560939B (en) 2014-12-01 2014-12-01 A kind of preparation method of bacteria carrier particle

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410717114.8A CN104560939B (en) 2014-12-01 2014-12-01 A kind of preparation method of bacteria carrier particle

Publications (2)

Publication Number Publication Date
CN104560939A CN104560939A (en) 2015-04-29
CN104560939B true CN104560939B (en) 2018-03-13

Family

ID=53078019

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410717114.8A Expired - Fee Related CN104560939B (en) 2014-12-01 2014-12-01 A kind of preparation method of bacteria carrier particle

Country Status (1)

Country Link
CN (1) CN104560939B (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105039300A (en) * 2015-08-19 2015-11-11 浙江工业大学 Preparation method of heterogeneous bacteria embedding particles
CN111333200B (en) * 2020-03-18 2022-07-05 运城学院 Embedded immobilized microorganism particles, preparation method and sewage treatment method

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101544970A (en) * 2009-05-08 2009-09-30 周鑫 Immobilized carrier of core-shell composite structure and its preparing process
CN101768583A (en) * 2010-01-22 2010-07-07 中国海洋大学 Method for immobilizing oil degradation bacteria with reed straw as carrier and application thereof
CN101875928A (en) * 2009-04-29 2010-11-03 中国环境科学研究院 Embedding immobilization method for microbial preparation
CN103212449A (en) * 2013-04-15 2013-07-24 沈阳三聚凯特催化剂有限公司 Hydrofining catalyst carrier and preparation method thereof as well as hydrofining catalyst using carrier and preparation method of hydrofining catalyst

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101875928A (en) * 2009-04-29 2010-11-03 中国环境科学研究院 Embedding immobilization method for microbial preparation
CN101544970A (en) * 2009-05-08 2009-09-30 周鑫 Immobilized carrier of core-shell composite structure and its preparing process
CN101768583A (en) * 2010-01-22 2010-07-07 中国海洋大学 Method for immobilizing oil degradation bacteria with reed straw as carrier and application thereof
CN103212449A (en) * 2013-04-15 2013-07-24 沈阳三聚凯特催化剂有限公司 Hydrofining catalyst carrier and preparation method thereof as well as hydrofining catalyst using carrier and preparation method of hydrofining catalyst

Also Published As

Publication number Publication date
CN104560939A (en) 2015-04-29

Similar Documents

Publication Publication Date Title
Lapponi et al. Cell immobilization strategies for biotransformations
Margaritis et al. Advances in ethanol production using immobilized cell systems
CN105368745B (en) Composite microbial preparation for treating black and odorous rivers and preparation method thereof
CN101875928A (en) Embedding immobilization method for microbial preparation
CN108018280B (en) Construction method of microorganism slow-release carrier
CN103896407B (en) A kind of quick startup, biofilm carbon antimicrobial composition process for purifying water
CN109775860A (en) A kind of fixed microorganism carrier filler and preparation method thereof
CN104528947B (en) A kind of modification biological enzyme charcoal filler for sewage disposal
CN102583772B (en) Microbial preparation comprising mixed microorganisms (bm-s-1), and a biological treatment method for rivers and lakes and a sludge autodigestion process using the same
US20060188978A1 (en) Products and processes for waste control
CN105039300A (en) Preparation method of heterogeneous bacteria embedding particles
CN105347513B (en) A kind of preparation method and applications of probiotics
CN101591069A (en) The treatment process of polluted lake water body
CN101591131B (en) Method for treating bottom sediment in lake
CN103255123B (en) Method for mycelium pellet to form mixed mycelium pellet by adsorbing photosynthetic bacteria
CN102757951A (en) Building and papermaking wastewater treatment method of marine double-fungus co-immobilized system
CN102703413B (en) Method for immobilizing photosynthetic bacteria by using mycelium pellets as biological carrier
CN104560939B (en) A kind of preparation method of bacteria carrier particle
CN102190377A (en) Floating water surface oil stain processor
Chen et al. Encapsulation technology to improve biological resource recovery: recent advancements and research opportunities
Vasilieva et al. Biotechnological Applications of Immobilized Microalgae
CN108946933B (en) A kind of modified poly ethylene microbe carrier stuffing
CN110734138A (en) In-situ treatment method for freshwater aquaculture wastewater
CN102199561A (en) Aerobic denitrifying bacterium treating nitrite as nitrogen source and screening method thereof
CN106830344B (en) Biological water purification system

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20180313

CF01 Termination of patent right due to non-payment of annual fee