CN104845905A - High-efficiency composite inocula for removing salad oil-containing waste water COD and application thereof - Google Patents
High-efficiency composite inocula for removing salad oil-containing waste water COD and application thereof Download PDFInfo
- Publication number
- CN104845905A CN104845905A CN201510136994.4A CN201510136994A CN104845905A CN 104845905 A CN104845905 A CN 104845905A CN 201510136994 A CN201510136994 A CN 201510136994A CN 104845905 A CN104845905 A CN 104845905A
- Authority
- CN
- China
- Prior art keywords
- candida tropicalis
- salad oil
- serratia
- bacterium amount
- inocula
- 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.)
- Granted
Links
- 239000002351 wastewater Substances 0.000 title claims abstract description 48
- 240000008415 Lactuca sativa Species 0.000 title claims abstract description 39
- 235000012045 salad Nutrition 0.000 title claims abstract description 39
- 239000002131 composite material Substances 0.000 title claims abstract description 31
- 241000894006 Bacteria Species 0.000 claims abstract description 66
- 241000222178 Candida tropicalis Species 0.000 claims abstract description 47
- 241000607715 Serratia marcescens Species 0.000 claims abstract description 28
- 239000003795 chemical substances by application Substances 0.000 claims description 30
- 241000233866 Fungi Species 0.000 claims description 26
- 241000607720 Serratia Species 0.000 claims description 24
- 238000000034 method Methods 0.000 claims description 21
- 239000007788 liquid Substances 0.000 claims description 12
- 238000011081 inoculation Methods 0.000 claims description 11
- 230000001580 bacterial effect Effects 0.000 claims description 10
- 239000001888 Peptone Substances 0.000 claims description 8
- 239000002609 medium Substances 0.000 claims description 8
- 239000002054 inoculum Substances 0.000 claims description 7
- 229940041514 candida albicans extract Drugs 0.000 claims description 6
- 150000001875 compounds Chemical class 0.000 claims description 6
- 239000001963 growth medium Substances 0.000 claims description 6
- 239000012138 yeast extract Substances 0.000 claims description 6
- 108010080698 Peptones Proteins 0.000 claims description 5
- 235000015097 nutrients Nutrition 0.000 claims description 5
- 235000019319 peptone Nutrition 0.000 claims description 5
- WQZGKKKJIJFFOK-GASJEMHNSA-N Glucose Natural products OC[C@H]1OC(O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-GASJEMHNSA-N 0.000 claims description 4
- 239000008121 dextrose Substances 0.000 claims description 4
- 239000000843 powder Substances 0.000 claims description 4
- 238000002360 preparation method Methods 0.000 claims description 4
- 235000015278 beef Nutrition 0.000 claims description 3
- 239000004519 grease Substances 0.000 abstract description 9
- 239000010865 sewage Substances 0.000 abstract description 9
- 239000000203 mixture Substances 0.000 abstract description 6
- 230000000593 degrading effect Effects 0.000 abstract description 4
- 238000002474 experimental method Methods 0.000 abstract description 2
- 238000012545 processing Methods 0.000 abstract description 2
- 239000010802 sludge Substances 0.000 abstract description 2
- 241001622809 Serratia plymuthica Species 0.000 abstract 1
- 238000009472 formulation Methods 0.000 abstract 1
- 239000003921 oil Substances 0.000 description 34
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 18
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 14
- 239000002699 waste material Substances 0.000 description 8
- 239000011780 sodium chloride Substances 0.000 description 7
- 244000005700 microbiome Species 0.000 description 6
- 239000000243 solution Substances 0.000 description 6
- 230000009897 systematic effect Effects 0.000 description 5
- 239000012153 distilled water Substances 0.000 description 4
- 238000004321 preservation Methods 0.000 description 4
- 238000000926 separation method Methods 0.000 description 4
- 102000016938 Catalase Human genes 0.000 description 3
- 108010053835 Catalase Proteins 0.000 description 3
- 241000237502 Ostreidae Species 0.000 description 3
- 240000004808 Saccharomyces cerevisiae Species 0.000 description 3
- 230000015556 catabolic process Effects 0.000 description 3
- 238000006731 degradation reaction Methods 0.000 description 3
- 239000002068 microbial inoculum Substances 0.000 description 3
- 230000000877 morphologic effect Effects 0.000 description 3
- 235000020636 oyster Nutrition 0.000 description 3
- 238000012797 qualification Methods 0.000 description 3
- 238000012216 screening Methods 0.000 description 3
- FRXSZNDVFUDTIR-UHFFFAOYSA-N 6-methoxy-1,2,3,4-tetrahydroquinoline Chemical compound N1CCCC2=CC(OC)=CC=C21 FRXSZNDVFUDTIR-UHFFFAOYSA-N 0.000 description 2
- 241000726221 Gemma Species 0.000 description 2
- 108090001060 Lipase Proteins 0.000 description 2
- 102000004882 Lipase Human genes 0.000 description 2
- 239000004367 Lipase Substances 0.000 description 2
- 238000012408 PCR amplification Methods 0.000 description 2
- 241001285450 Serratia sp. SH-AB-1 Species 0.000 description 2
- 229920002472 Starch Polymers 0.000 description 2
- 241001052560 Thallis Species 0.000 description 2
- 230000010165 autogamy Effects 0.000 description 2
- 238000005842 biochemical reaction Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000000855 fermentation Methods 0.000 description 2
- 230000004151 fermentation Effects 0.000 description 2
- 230000007062 hydrolysis Effects 0.000 description 2
- 238000006460 hydrolysis reaction Methods 0.000 description 2
- 235000019421 lipase Nutrition 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 235000013372 meat Nutrition 0.000 description 2
- 230000035479 physiological effects, processes and functions Effects 0.000 description 2
- 235000019698 starch Nutrition 0.000 description 2
- 239000008107 starch Substances 0.000 description 2
- 238000012360 testing method Methods 0.000 description 2
- 235000013311 vegetables Nutrition 0.000 description 2
- 108020004465 16S ribosomal RNA Proteins 0.000 description 1
- 108020004463 18S ribosomal RNA Proteins 0.000 description 1
- 229920001817 Agar Polymers 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- 102000004190 Enzymes Human genes 0.000 description 1
- 108090000790 Enzymes Proteins 0.000 description 1
- 244000068988 Glycine max Species 0.000 description 1
- 235000010469 Glycine max Nutrition 0.000 description 1
- 241000607714 Serratia sp. Species 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000008272 agar Substances 0.000 description 1
- 239000007640 basal medium Substances 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000001311 chemical methods and process Methods 0.000 description 1
- 239000010779 crude oil Substances 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 238000004332 deodorization Methods 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 239000012634 fragment Substances 0.000 description 1
- 125000005908 glyceryl ester group Chemical group 0.000 description 1
- 235000021190 leftovers Nutrition 0.000 description 1
- 150000002632 lipids Chemical class 0.000 description 1
- 230000002906 microbiologic effect Effects 0.000 description 1
- 239000010815 organic waste Substances 0.000 description 1
- 235000010482 polyoxyethylene sorbitan monooleate Nutrition 0.000 description 1
- 229920000053 polysorbate 80 Polymers 0.000 description 1
- 238000002203 pretreatment Methods 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 238000007670 refining Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000005070 sampling Methods 0.000 description 1
- 238000003375 selectivity assay Methods 0.000 description 1
- 238000012163 sequencing technique Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000005728 strengthening Methods 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 238000002255 vaccination Methods 0.000 description 1
- 244000298073 white hoary pea Species 0.000 description 1
Landscapes
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
The invention discloses a high-efficiency composite inocula for removing salad oil-containing waste water COD and an application thereof. The composite inocula is composed of four high efficiency grease degrading bacteria, and are respectively candida tropicalis HY-A-3, serratia plymuthica SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2. According to the invention, a bacterium source sample is collected from activated sludge and restaurant sewer sewage in a sewage treatment factory, single bacterium capable of removing salad oil waste water COD with high efficiency can be screened by separating; then the high efficiency composite inocula is constructed through a complex formulation experiments, and the result is characterized in that an inocula combination of HY-A-3, SH-AB-1, SZ2-A-3 and LB1-AB-2 has the highest COD clearance rate. When the concentration of the composite inocula is 1-5%, the inocula combination has more than 75% on salad oil waste water COD clearance. The inocula has good application prospect and value in during salad oil waste water processing engineering.
Description
Technical field
The present invention relates to a kind of high efficiency composition microbial inoculum removed containing salad oil wastewater COD, also relate to the composite fungus agent application method removing salad oil wastewater COD.
Background technology
Along with salad oil demand sharply rises, the highly concentrated oil-bearing wastewater in salad oil processing causes concern on the impact that environment causes.Salad oil manufacturing wastewater refer to the squeezing such as soybean or the crude oil that leaches gained are come unstuck, depickling, decolouring, deodorization, dewaxing, de-ester etc. process the waste water produced.Produce a large amount of organic waste water in this refining process, the feature of this waste water is high COD (ρ
cODcan more than 10000mg/L be reached), the large (ρ of oil-contg
oilcan more than 3000mg/L be reached), B/C 0.5-0.6.At present physico-chemical process pre-treatment oil removing and activated sludge process or anaerobic technique process are adopted more for the process of salad oil manufacturing wastewater.After amount of grease enters Sewage treatment systems, usually can cause producing bubble, and hyphomycetic growth can be promoted, affect the operation of sewage disposal biochemical system.Therefore be the deoiling function of the biochemical system in strengthening salad oil wastewater treating processes, accelerate the degraded to grease, the possibility that the water outlet of reduction system exceeds standard, reduce the foam produced, core---the enhancement microbiological of salad oil wastewater process provided by the invention, utilize the functional flora screening yeast and the bacterium formation obtained from occurring in nature, in aerobic biological treatment process, efficient-decomposition is carried out to the lipid acid of high density, glyceryl ester and other organism, to realize the effluent quality improving Sewage treatment systems.
Summary of the invention
For defect of the prior art, the object of this invention is to provide composite fungus agent of a kind of efficient removal salad oil wastewater COD and preparation method thereof.
Another object of the present invention is to provide the application method of above-mentioned composite fungus agent.
In order to realize foregoing invention object, the technical solution used in the present invention is as follows:
Remove the composite fungus agent containing salad oil wastewater COD, it is characterized in that, described composite fungus agent comprises bacterial strain: candida tropicalis HY-A-3, CGMCC No.10424; Serratia SH-AB-1, CGMCCNo.10427; Candida tropicalis SZ2-A-3, CGMCC No.10425; Serratia marcescens LB1-AB-2, CGMCC No.10426.
Further, the bacterium amount of described candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 accounts for 25-45%, 25-45%, 8-25% and 2-25% of total bacterium amount volume respectively.
Further, the bacterium amount of described candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 accounts for 30-40%, 30-40%, 15-20%, 3-20% of total bacterium amount volume respectively.
Further, the bacterium amount of described candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 accounts for 33%, 33%, 17%, 17% of total bacterium amount volume respectively.
Present invention also offers a kind of preparation method removing the composite fungus agent containing salad oil wastewater COD, comprise the following steps: get the mono-colony inoculation of candiyeast HY-A-3 and SZ2-A-3 respectively in 100mL yeast extract powder peptone dextrose culture-medium, get Serratia SH-AB-1 and the mono-colony inoculation of serratia marcescens LB1-AB-2 in 100mL beef extract-peptone liquid nutrient medium, at 180rpm, shaking culture 18h at 28 DEG C; The four strain bacterium cultivating 18h are carried out compound.
Present invention also offers a kind of method removed containing salad oil wastewater COD, comprise the steps: the composite fungus agent comprising candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 to be inoculated in salad oil wastewater by the proportioning of 25-45%, 25-45%, 8-25% and 2-25% of accounting for total bacterium amount volume respectively, and cultivate 2 ~ 3 days.
Further, the bacterium amount of described candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 accounts for 30-40%, 30-40%, 15-20% and 3-20% of total bacterium amount volume respectively.
Further, the bacterium amount of described candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 accounts for 33%, 33%, 17% and 17% of total bacterium amount volume respectively.
Further, described composite fungus agent is with the inoculation of bacterium liquid form, and its inoculum size is the 1-5% (v/v) of process wastewater volume.
Further, described inoculum size is the 1.5-2.5% (v/v) of process wastewater volume.
Effect of the present invention is: adopt composite fungus agent of the present invention and application thereof, can reach more than 75% to the clearance containing salad oil wastewater COD.
Accompanying drawing explanation
The systematic evolution tree of Fig. 1 candida tropicalis Candida tropicalis HY-A-3;
The systematic evolution tree of Fig. 2 Serratia Serratia sp.SH-AB-1;
The systematic evolution tree of Fig. 3 candida tropicalis Candida tropicalis SZ2-A-3;
The systematic evolution tree of Fig. 4 serratia marcescens Serratia marcescens LB1-AB-2.
Classification And Nomenclature: candida tropicalis, Latin name: Candida tropicalis HY-A-3
Preservation date: on January 22nd, 2015;
Depositary institution's full name and abbreviation: China Committee for Culture Collection of Microorganisms's common micro-organisms center (CGMCC)
Deposit number: CGMCC No.10424;
Classification And Nomenclature: Serratia, Latin name: Serratia sp.SH-AB-1
Preservation date: on January 22nd, 2015;
Depositary institution: China Committee for Culture Collection of Microorganisms's common micro-organisms center (CGMCC)
Deposit number: CGMCC No.10427;
Classification And Nomenclature: candida tropicalis, Latin name: Candida tropicalis SZ2-A-3
Preservation date: on January 22nd, 2015;
Depositary institution: China Committee for Culture Collection of Microorganisms's common micro-organisms center (CGMCC)
Deposit number: CGMCC No.10425;
Classification And Nomenclature: serratia marcescens, Latin name: Serratia marcescens LB1-AB-2
Preservation date: on January 22nd, 2015;
Depositary institution: China Committee for Culture Collection of Microorganisms's common micro-organisms center (CGMCC)
Deposit number: CGMCC No.10426;
Embodiment
Below illustrate the present invention, but the protection domain be not intended to limit the present invention.
In order to solve the problem, the present invention gathers the samples such as certain dining room, shopping center effluent sewerage, other lower ditch, market of farm produce meat stand sewage, sewage work's biochemical reaction tank mud and the other body refuse of certain vegetables oil source mill treatment tank, through enrichment, domestication, separation, purifying, filter out the pure bacterial strain having and remove salad oil wastewater COD, again through primary dcreening operation, multiple sieve, select efficient function yeast, build the composite fungus agent removing salad oil wastewater COD.
HY-A-3 in the present invention is located away from certain dining room, shopping center effluent sewerage; SH-AB-1 is located away from the sewage of other lower ditch, meat stand, the market of farm produce, Beijing; SZ2-A-3 is located away from Hebei sewage work biochemical reaction tank mud; LB1-AB-2 is located away from the other body refuse of Beijing vegetables oil source mill treatment tank.Morphological specificity observation and the qualification of part Physiology and biochemistry are carried out respectively to 4 strain bacterium in composite fungus agent.HY-A-3 thalli morphology ovalize, size is about 5 ~ 6 × 7 ~ 9 μm,, oyster white, smooth, protruding, neat in edge rounded at the upper bacterium colony of yeast extract powder peptone dextrose culture-medium (YPD substratum), still can better grow in the NaCl solution of 10%; SH-AB-1 thalline is rod-short, and size is about 0.5 ~ 0.8 × 0.9 ~ 1.3 μm, without gemma, bacterium colony is rounded, protruding, smooth, oyster white, Gram-negative, and catalase is positive, Starch Hydrolysis is negative, can not grow in the NaCl solution more than 7% concentration; SZ2-A-3 thalli morphology ovalize, size is about 5 ~ 7 × 8 ~ 9 μm, circular, smooth, protruding, the oyster white of bacterium colony on YPD substratum, and catalase is positive, still can better grow in the NaCl solution of 10%; LB1-AB-2 thalline is rod-short, and size is about 0.5 ~ 0.8 × 0.6 ~ 1.0 μm, and without gemma, bacterium colony is circular, smooth, protruding, red, Gram-negative, and catalase is positive, and Starch Hydrolysis is negative, can not grow in the NaCl solution more than 7% concentration.Carry out molecular biology identification respectively to 4 strain bacterium, HY-A-3 and SZ2-A-3 carries out the pcr amplification of 18S rDNA after extracting gene DNA, SH-AB-1 and LB1-AB-2 carries out the pcr amplification of 16S rDNA, the fragment of acquisition is used for order-checking.After order-checking, sequence results carries out Blast comparison in Genbank, and constructing system evolutionary tree, as Figure 1-Figure 4.
By the systematic evolution tree of sequencing result and structure, in conjunction with 4 strain bacterium morphological specificitys, growth conditions, Physiology and biochemistry qualification result, can preliminary evaluation bacterial strain HY-A-3 and SZ2-A-3 be candida tropicalis (Candidatropicalis), LB1-AB-2 is that serratia marcescens (Serratia marcescens), SH-AB-1 belong to serratia (Serratia sp.).Above-mentioned four kinds of bacterial strains are all deposited in China Committee for Culture Collection of Microorganisms's common micro-organisms center (address: No. 3, Yard 1, BeiChen xi Road, Chaoyang District, Beijing City).
In composite fungus agent of the present invention, the bacterium amount of candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3, serratia marcescens LB1-AB-2 accounts for 25-45%, 25-45%, 8-25% and 2-25% of total bacterium amount volume respectively, preferably accounts for 30-40%, 30-40%, 15-20% and 3-20% of total bacterium amount volume respectively.
The preparation method of above-mentioned composite fungus agent is, get the mono-colony inoculation of candiyeast HY-A-3 and SZ2-A-3 respectively in 100mL yeast extract powder peptone dextrose culture-medium (YPD liquid nutrient medium), get Serratia SH-AB-1 and the mono-colony inoculation of serratia marcescens LB1-AB-2 in 100mL beef extract-peptone liquid nutrient medium, at 180rpm, shaking culture 18h at 28 DEG C.Candida tropicalis HY-A-3, the Serratia SH-AB-1, candida tropicalis SZ2-A-3, the serratia marcescens LB1-AB-2 that cultivate 18h are carried out compound by bacterium amount than 30-40%, 30-40%, 15-20% and the 3-20% accounting for total bacterium amount volume.
The application of above-mentioned composite fungus agent, is inoculated in containing salad oil mass by composite fungus agent by the concentration of 1-5% and is the oil wastewater of 1000-2000mg/L, can reaches more than 75% to the clearance of waste water COD.
Embodiment 1: the acclimating of grease degrading strain and separation screening.
First the present invention gathers rich grease-contained bacterium source, many places sample, then carries out acclimating cultivation to bacterium source sample respectively, more therefrom isolates pure bacterial strain, then obtains high-efficiency grease degradation bacteria through primary dcreening operation, multiple sieve.
Concrete implementation step is as follows:
(1) acclimating of grease degrading strain is cultivated and initial gross separation
Get 3g mud sample or 3mL water sample, be inoculated in the triangular flask containing 100mL enrichment culture liquid, and 28 DEG C, cultivate 3d in the shaking table of 180rpm.Get the bacterium liquid after 3mL enrichment, be inoculated in and tame in the triangular flask of nutrient solution containing 100mL, 28 DEG C, 180rpm shaking table is cultivated, and 3d is 1 cycle, is moved to by bacterium liquid on new domestication substratum and cultivate after each cycle terminates.
Get the bacterium liquid after 1mL domestication, be inoculated in respectively containing in 100mL bacterium or yeast liquid basal medium, be placed in 28 DEG C, the shaking table of 180rpm is cultivated.After 3d, after the bacterium liquid gradient dilution of cultivation, coat in corresponding solid-based basal culture medium flat board respectively, cultivate 48-72h at 30 DEG C of incubators.The microorganism strains of picking colony morphological specificity significant difference, streak inoculation is in the basic medium of correspondence respectively, 30 DEG C of constant temperature culture 48-72h, and obtain single bacterium colony pure growth through repeating line separation, inclined-plane is preserved.
(2) screening of high-efficiency grease degradation bacteria
Line is separated the bacterial strain point obtained to receive on lipase checking culture medium flat plate, 30 DEG C of constant incubators cultivate 48-72h, just sift out the bacterial strain that transparent circle diameter is larger, for next step multiple sieve provides foundation.
With colony inoculation in transfering loop picking primary dcreening operation flat board in the triangular flask containing 100mL basic medium, 28 DEG C, the cultivation of 180rpm shaking table, transfer in the triangular flask containing 100mL salad oil wastewater by 2% inoculum size after cultivating 18h, 28 DEG C, 180rpm shaker fermentation, respectively at 48h, 72h sampling and measuring COD.Last combining fat enzyme circle proof test, obtains the stronger bacterial strain of 8 strain degraded grease ability.
In the present invention, required medium preparing is as follows:
1. enrichment medium: K
2hPO
43g, NaCl 5g, MgSO
47H
2o 0.5g, peptone 10g, yeast extract paste 5g, salad oil 10g, distilled water 1000mL, pH=7.2.
2. substratum is tamed: yeast extract paste 1g, (NH
4)
2sO
43g, K
2hPO
41g, NaH
2pO
41g, NaCl0.5g, MgSO
47H
2o 0.2g, salad oil adds 5g, 10g, 15g successively, distilled water 1000mL, pH7.0.
3. lipase checking substratum: KH
2pO
40.3g, MgSO
47H
2o 0.1g, K
2hPO
41.5g, (NH
4)
2sO
41g, NaCl 5g, FeSO
47H
2o 0.01g, Tween 80 20mL, salad oil 6g, agar 18g, distilled water 1000mL, pH7.0.
4. autogamy oily(waste)water: KH
2pO
40.3g, MgSO
47H
2o 0.1g, K
2hPO
41.5g, (NH
4)
2sO
41g, NaCl 5g, FeSO
47H
2o 0.01g, salad oil 2g, distilled water 1000mL, pH7.0.
Embodiment 2: the structure of composite fungus agent in the present invention.
Filter out 8 plant height effect grease degrading strains, combine experiment is carried out in choosing wherein 4 strains, and in often kind of combination, 4 kinds of bacterium bacterium amount ratios are identical, be inoculated in autogamy oily(waste)water, measure the COD of salad oil wastewater after 72h by total inoculum size 2%.The combination of what COD clearance was the highest be combined as HY-A-3, SH-AB-1, SZ2-A-3 and LB1-AB-2, its COD clearance is 80.18%, through qualification, 4 strain bacterium are respectively candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3, serratia marcescens LB1-AB-2.In aforesaid combination 4 kind of bacterium is carried out to four factor three horizontal quadrature tests of different vaccination ratio.Research shows, between each bacterial strain, best inoculation volume proportion HY-A-3:SH-A-1:SZ2-A-3:LB1-AB-2 is 33%, 33%, 17% and 17%, the total bacterium amount of mix bacterium agent is inoculated in oily(waste)water by the inoculative proportion of 2%, and after 72h, oil wastewater COD clearance is 81.3% (former water COD1426.2mg/L).
Embodiment 3: be with above-described embodiment difference, 25%, 25%, 25% and 25% proportioning that candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 tetra-strain bacterium account for total bacterium amount volume by bacterium amount is respectively carried out compound, mix bacterium agent is seeded in oily(waste)water in the ratio of 1%, after 72h, oil wastewater COD clearance is 75.98% (former water COD1076.32mg/L).
Embodiment 4: be with above-described embodiment difference, 45%, 45%, 8% and 2% proportioning that candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 tetra-strain bacterium account for total bacterium amount volume by bacterium amount is respectively carried out compound, mix bacterium agent is seeded in oily(waste)water in the ratio of 5%, after 72h, oil wastewater COD clearance is 80.15% (former water COD1058.49mg/L).
Embodiment 5: in the present invention, composite fungus agent is tested actual oil wastewater COD degradation.
Actual waste water takes from certain Peasants Joy food and drink waste water, and crossed two-layer gauze removing dish leaf leftovers before using, the initial COD of waste water is 1723.6mg/L, pH is 6.0.Get the actual oily(waste)water of 100mL in 250mL triangular flask, after regulating pH to 7.2, by 2% inoculum size inoculating compound bacterium agent, setting does not inoculate the oily(waste)water of microbial inoculum in contrast, with being placed in 180rpm, 28 DEG C of condition bottom fermentations cultivations, measures COD after 72h.The clearance of composite fungus agent to actual oily(waste)water COD is 78.95%.
It should be noted that; above-mentioned specific embodiment is only exemplary; under above-mentioned instruction of the present invention, those skilled in the art can carry out various improvement and distortion on the basis of above-described embodiment, and these improve or distortion drops in protection scope of the present invention.It will be understood by those skilled in the art that specific descriptions are above to explain object of the present invention, not for limiting the present invention.Protection scope of the present invention is by claim and equivalents thereof.
Claims (10)
1. remove the composite fungus agent containing salad oil wastewater COD, it is characterized in that, described composite fungus agent comprises bacterial strain: candida tropicalis HY-A-3, CGMCC No.10424; Serratia SH-AB-1, CGMCCNo.10427; Candida tropicalis SZ2-A-3, CGMCC No.10425; Serratia marcescens LB1-AB-2, CGMCC No.10426.
2. a kind of composite fungus agent removed containing salad oil wastewater COD according to claim 1, is characterized in that: the bacterium amount of described candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 accounts for 25-45%, 25-45%, 8-25% and 2-25% of total bacterium amount volume respectively.
3. a kind of composite fungus agent removed containing salad oil wastewater COD according to claim 2, is characterized in that: the bacterium amount of described candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 accounts for 30-40%, 30-40%, 15-20% and 3-20% of total bacterium amount volume respectively.
4. a kind of composite fungus agent removed containing salad oil wastewater COD according to claim 3, is characterized in that: the bacterium amount of described candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 accounts for 33%, 33%, 17% and 17% of total bacterium amount volume respectively.
5. the preparation method of the composite fungus agent described in the arbitrary claim of claim 1-4, comprise the following steps: get the mono-colony inoculation of candiyeast HY-A-3 and SZ2-A-3 respectively in 100mL yeast extract powder peptone dextrose culture-medium, get Serratia SH-AB-1 and the mono-colony inoculation of serratia marcescens LB1-AB-2 in 100mL beef extract-peptone liquid nutrient medium, at 180rpm, shaking culture 18h at 28 DEG C; The four strain bacterium cultivating 18h are carried out compound.
6. remove the method containing salad oil wastewater COD for one kind, comprise the steps: the composite fungus agent comprising candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 to be inoculated in salad oil wastewater by 25-45%, 25-45%, 8-25% and 2-25% proportioning accounting for total bacterium amount volume respectively, and cultivate 2 ~ 3 days.
7. a kind of method removed containing salad oil wastewater COD according to claim 6, is characterized in that: the bacterium amount of described candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 accounts for 30-40%, 30-40%, 15-20% and 3-20% of total bacterium amount volume respectively.
8. a kind of method removed containing salad oil wastewater COD as claimed in claim 7, is characterized in that: the bacterium amount of described candida tropicalis HY-A-3, Serratia SH-AB-1, candida tropicalis SZ2-A-3 and serratia marcescens LB1-AB-2 accounts for 33%, 33%, 17% and 17% of total bacterium amount volume respectively.
9. a kind of method removed containing salad oil wastewater COD as described in claim 6,7 or 8, is characterized in that: described composite fungus agent is with the inoculation of bacterium liquid form, and its inoculum size is the 1-5% (v/v) of process wastewater volume.
10. a kind of method removed containing salad oil wastewater COD as claimed in claim 9, is characterized in that: described inoculum size is the 1.5-2.5% (v/v) of process wastewater volume.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510136994.4A CN104845905B (en) | 2015-03-26 | 2015-03-26 | The high efficiency composition microbial inoculum of removal COD containing salad oil wastewater a kind of and its application |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510136994.4A CN104845905B (en) | 2015-03-26 | 2015-03-26 | The high efficiency composition microbial inoculum of removal COD containing salad oil wastewater a kind of and its application |
Publications (2)
Publication Number | Publication Date |
---|---|
CN104845905A true CN104845905A (en) | 2015-08-19 |
CN104845905B CN104845905B (en) | 2018-02-16 |
Family
ID=53845897
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201510136994.4A Active CN104845905B (en) | 2015-03-26 | 2015-03-26 | The high efficiency composition microbial inoculum of removal COD containing salad oil wastewater a kind of and its application |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN104845905B (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108441444A (en) * | 2018-03-22 | 2018-08-24 | 中电建水环境治理技术有限公司 | A kind of complex micro organism fungicide administered suitable for black and odorous water |
CN110938557A (en) * | 2019-11-01 | 2020-03-31 | 湖南景翌湘台环保高新技术开发有限公司 | Composite microbial inoculum for degrading COD (chemical oxygen demand) in wastewater and preparation method thereof |
CN112920958A (en) * | 2021-03-03 | 2021-06-08 | 江苏宜裕环保科技有限公司 | High-concentration wastewater biological pretreatment functional bacteria and application thereof |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2011182782A (en) * | 2010-02-09 | 2011-09-22 | Sekisui Aqua System Kk | Oil-and-fat splitting microorganism, microorganism-immobilization carrier, method for treating waste water and system for treating waste water |
WO2012160526A2 (en) * | 2011-05-23 | 2012-11-29 | Ofir Menashe | Formulations of microorganism comprising particles and uses of same |
CN104031851A (en) * | 2014-02-28 | 2014-09-10 | 中国科学院南海海洋研究所 | Candida tropicalis Y2 and applications thereof |
CN104371951A (en) * | 2014-09-15 | 2015-02-25 | 河北省科学院生物研究所 | Serratia sp. A5 and uses thereof |
-
2015
- 2015-03-26 CN CN201510136994.4A patent/CN104845905B/en active Active
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2011182782A (en) * | 2010-02-09 | 2011-09-22 | Sekisui Aqua System Kk | Oil-and-fat splitting microorganism, microorganism-immobilization carrier, method for treating waste water and system for treating waste water |
WO2012160526A2 (en) * | 2011-05-23 | 2012-11-29 | Ofir Menashe | Formulations of microorganism comprising particles and uses of same |
CN104031851A (en) * | 2014-02-28 | 2014-09-10 | 中国科学院南海海洋研究所 | Candida tropicalis Y2 and applications thereof |
CN104371951A (en) * | 2014-09-15 | 2015-02-25 | 河北省科学院生物研究所 | Serratia sp. A5 and uses thereof |
Non-Patent Citations (4)
Title |
---|
K. CHIGUSA等: "Treatment of wastewater from oil manufacturing plant by yeasts", 《WATER SCIENCE AND TECHNOLOGY》 * |
SPYRIDON NTOUGIAS 等: "The Microbiology of Olive Mill Wastes", 《BIOMED RESEARCH INTERNATIONAL》 * |
吕文洲 等: "酵母菌处理高浓度含油废水的研究", 《工业水处理》 * |
韩云 等: "五株分离酵母菌的甘油酯和脂肪酸降解活性比较", 《中国环境科学》 * |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108441444A (en) * | 2018-03-22 | 2018-08-24 | 中电建水环境治理技术有限公司 | A kind of complex micro organism fungicide administered suitable for black and odorous water |
CN108441444B (en) * | 2018-03-22 | 2020-09-25 | 中电建生态环境集团有限公司 | Compound microbial agent suitable for black and odorous water treatment |
CN110938557A (en) * | 2019-11-01 | 2020-03-31 | 湖南景翌湘台环保高新技术开发有限公司 | Composite microbial inoculum for degrading COD (chemical oxygen demand) in wastewater and preparation method thereof |
CN112920958A (en) * | 2021-03-03 | 2021-06-08 | 江苏宜裕环保科技有限公司 | High-concentration wastewater biological pretreatment functional bacteria and application thereof |
Also Published As
Publication number | Publication date |
---|---|
CN104845905B (en) | 2018-02-16 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Ahmad et al. | Treatment and utilization of dairy industrial waste: A review | |
CN104862244B (en) | A kind of high efficiency composition microbial inoculum for removing the oil wastewater COD containing mixing and its application | |
CN103602616B (en) | Bacillus amyloliquefaciens Y10 and application thereof | |
CN111117939B (en) | Thermophilic aerophilic thiamine-decomposing bacillus and application thereof | |
CN105132323B (en) | One plant of salt tolerant bacillus and its application in high-salt wastewater processing | |
CN110317733B (en) | Geotrichum woodland strain and application thereof in degradation of kitchen waste | |
CN108220169B (en) | Separation screening and identification method of strain for degrading polystyrene | |
CN103642729B (en) | Method for producing Bacillus subtilis for feeds by fermenting high-salt-content amino acid wastewater | |
CN104830942A (en) | Biological alcohol production technique of organic sewage | |
CN104371951B (en) | A kind of Serratieae A5 and application thereof | |
CN102533562A (en) | Rhizopus oryzae TY GF1 bacterial strain and application thereof in degrading high-concentration oil in catering waste water | |
CN104959367B (en) | Kitchen waste treatment process | |
CN104087525A (en) | Novel seawater fermentation strain generating biosurfactant | |
CN104845905A (en) | High-efficiency composite inocula for removing salad oil-containing waste water COD and application thereof | |
CN105254024A (en) | Method for preparing garbage enzyme from fruits | |
CN102250776A (en) | Acid-resistance heterotrophic bacterium strain Z3 used for bioleaching treatment of sludge and livestock and poultry manure | |
CN106119150B (en) | A kind of dephosphorization microbial bacterial agent and its preparation method and application | |
CN107285482A (en) | A kind of environmental protection ferment of purifying eutrophic water quality and preparation method thereof | |
CN115353210B (en) | Application of bacillus pumilus LZP02 in treatment of pig raising wastewater | |
JP2013116067A (en) | Fat and oil decomposing yeast and treatment method using the same | |
CN108911452A (en) | A method of improving citric acid wastewater dewatering performance of sludge using penicillium oxalicum | |
CN110272834B (en) | Odorless microbial agent for kitchen waste treatment and preparation method and application thereof | |
CN109052624A (en) | A kind of method and device of movable purifying sewage and black and odorous water | |
CN114410508A (en) | Grease degrading bacteria and screening method and application thereof | |
CN103642707B (en) | Method for producing candida for feeds by fermenting high-salt-content amino acid wastewater |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
EXSB | Decision made by sipo to initiate substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant | ||
CP01 | Change in the name or title of a patent holder | ||
CP01 | Change in the name or title of a patent holder |
Address after: 100025 6th Floor, West Wing Building, Sihui Building, 1008-B Huihe South Street, Sihui East, Chaoyang District, Beijing Patentee after: Beijing Beikong Industrial Environmental Technology Co.,Ltd. Address before: 100025 6th Floor, West Wing Building, Sihui Building, 1008-B Huihe South Street, Sihui East, Chaoyang District, Beijing Patentee before: BEIJING BEIHUA ZHONGQING ENVIRONMENTAL ENGINEERING TECHNOLOGY CO.,LTD. |