CN108424857A - A kind of research method of simultaneous foster pattern scenedesmus culture for waste water fume treatment - Google Patents

A kind of research method of simultaneous foster pattern scenedesmus culture for waste water fume treatment Download PDF

Info

Publication number
CN108424857A
CN108424857A CN201810340119.1A CN201810340119A CN108424857A CN 108424857 A CN108424857 A CN 108424857A CN 201810340119 A CN201810340119 A CN 201810340119A CN 108424857 A CN108424857 A CN 108424857A
Authority
CN
China
Prior art keywords
culture
scenedesmus
waste water
food wastewater
under
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201810340119.1A
Other languages
Chinese (zh)
Inventor
宋春风
邱依婷
张尔雅
孙亚伟
谢美莲
范智超
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.)
Tianjin University
Original Assignee
Tianjin University
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 Tianjin University filed Critical Tianjin University
Priority to CN201810340119.1A priority Critical patent/CN108424857A/en
Publication of CN108424857A publication Critical patent/CN108424857A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12NMICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
    • C12N1/00Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
    • C12N1/12Unicellular algae; Culture media therefor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/50Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • C02F3/322Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae use of algae
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/32Nature of the water, waste water, sewage or sludge to be treated from the food or foodstuff industry, e.g. brewery waste waters

Abstract

The present invention discloses a kind of research method of the simultaneous foster pattern scenedesmus culture for waste water fume treatment, mainly includes the following steps:Scenedesmus is inoculated with:Scenedesmus S.obliquus is inoculated in container, BBM culture mediums are added, inoculation volume is 10% (V inoculum/V culture mediums), is subsequently placed in light incubator and cultivates 10~15 days;Wastewater Pretreatment:Micro-filtration removes microorganism and suspended solid particles in waste water, and carries out 100~121 DEG C of high pressure sterilization processing;Basic culture experiment;And foster pattern culture experiment.Waste water flue gas is utilized and handles under this and foster pattern using scenedesmus, need not additionally add nutriment and can produce has cost-benefit biomass, is a kind of dual strategy of sustainable development.

Description

A kind of research method of simultaneous foster pattern scenedesmus culture for waste water fume treatment
Technical field
The present invention relates to biological treatment waste water technology fields, and in particular to a kind of simultaneous foster pattern for waste water fume treatment The research method of scenedesmus culture.
Background technology
In recent years, microalgae has obtained extensive concern, and is used for wastewater treatment, carbon dioxide discharge-reduction and bio-fuel life The processes such as production[1].Microalgae is combined with existing wastewater treatment, Pollutants in Wastewater can be efficiently reduced and be carried out at the same time life Substance produces.
Microalgae is CO2Seal a variety of advantages that provide up for safekeeping, photosynthetic efficiency can get height than terrestrial plant higher, biomass The product of value.[2]High concentration CO is released from different industrial circles2Exhaust gas, can be used as a kind of CO of economy2Source, for micro- The biomass of algae produces[3]
And under the conditions of support, microalgae can absorb inorganic and organic substrates by synchronous breathing and photosynthesis, while real Existing photoautotrophy and heterotrophic growth.[4]Food wastewater is rich in the nutriments such as nitrogen, phosphorus, calcium, iron, aluminium and total organic carbon, Ke Yizuo For a kind of effective organic wastewater come realize microalgae biomass produce.[5]Therefore, using food wastewater and from industrial High concentration CO2Mixotrophic cultivation pattern, can reach inexpensive benefit micro algae biomass production.
Most of research mainly utilizes CO at present2The production for carrying out biofuel feedstock is combined with municipal sewage, will be eaten Product wastewater application is very limited in the research of industrial wastewater.
Invention content
It is an object of the invention to overcome defect existing for above-mentioned background technology, provide a kind of for waste water fume treatment And the research method of foster pattern scenedesmus culture.
To solve technical problem mentioned above in the background art, technical scheme of the present invention:One kind being used for waste water flue gas The research method of the simultaneous foster pattern scenedesmus culture of processing, includes the following steps:
1) scenedesmus is inoculated with:Scenedesmus S.obliquus is inoculated in container, BBM culture mediums are added, inoculation volume is 10% (V inoculums/V culture mediums) is subsequently placed in light incubator and cultivates 10~15 days;
Condition of culture is:23~27 DEG C of temperature, white fluorescent illuminate 110~135 μm of ol.m2.s-1And it is passed through 0.5~ 1.0L.min-1Filtration sterilization air conditions under cultivate, absorbance of the scenedesmus suspension in matrix culture medium be adjusted to 0.5~ 1.0;
2) Wastewater Pretreatment:Micro-filtration removes microorganism and suspended solid particles in waste water, and carries out 100~121 DEG C of high pressures Sterilization treatment[6]
Wherein, waste water comes from secondary urban sewage MWW and food wastewater FW;
3) basic culture experiment:In BBM culture mediums, with 5% CO2Synthesis gas is cultivated under following condition of culture S.obliquus scenedesmus 6~10 days;
Condition of culture:23~27 DEG C of temperature, white fluorescent illuminate 110~135 μm of ol.m2.s-1
4) simultaneous foster pattern culture experiment:
(1) in aluminium means of press seals serum bottle, 300 milliliters of above-mentioned steps 2 are added) in sterilized processing secondary urban sewage MWW is inoculated with 3~5% (VInoculum/VWaste water), it is aided with food wastewater FW and flue gas CO2
(2) secondary urban sewage MWW filtrates are diluted with food wastewater FW, and the food wastewater FW bodies of 3 different levels are arranged Product diluted concentration is the CO of 0.5,1,2% and 3 different levels2A concentration of 5,10,14.1%;
(3) 12 sewage solution are prepared altogether:Secondary urban sewage MWW and food wastewater FW volume ratios are 100:0 (MWW, point Not in 5,10 and 14.1%CO2Under), 99.5:0.5 (FW0.5, in 5,10 and 14.1%CO2Under), 99:1 (FW1, in 5,10 and 14.1%CO2Under) and 98:2 (FW2, in 5,10 and 14.1% CO2Under);
(5) the sewage solution is placed in inoculation bottle, is cultivated in 150rpm, 27 DEG C of water bath, white fluorescent shines Bright intensity is 120 μm of ol.m2.s-1Culture 6 days.
Micro-filtration uses 0.2 μm of nylon in the step 2)[7]
CO in the step 3)2Synthesis gas is by 5%CO2And 95%N2Composition.
Compared with prior art, the present invention has the advantage that:The present invention obtained secondary urban sewage by culture in 6 days (MWW) it is diluted with 0.5~1% food wastewater (FW), the highest growth of scenedesmus is supported under 10~14.1% carbon dioxide 0.42~0.44g.L-1, TN nutrient removals are up to 21~22mg.L-1, lipid production rate is 10~11mg.L-1.d-1And carbon water Production of chemicals rate is 13~16mg.L-1.d-1.Food wastewater is respectively by the aliphatic acid in scenedesmus, palmitic acid and oleic acid content It is increased to 8% and 6%.Therefore, food wastewater and exhaust gas CO2Application scenedesmus can be promoted to grow, improve lipid/carbon aquation Close the productivity and sewage treating efficiency of object.
Utilize and handle waste water flue gas under this and foster pattern using scenedesmus, need not additionally add nutriment and Can produce has cost-benefit biomass, is a kind of dual strategy of sustainable development.
Description of the drawings
Fig. 1 is FW and three difference COs of the S.obliquus in different diluted concentrations2Schematic diagram is grown under concentration level:
(a) undiluted secondary urban sewage MWW is represented;
(b) the food wastewater FW0.5 that dilution volume is 0.5% is represented;
(c) the food wastewater FW1 that dilution volume is 1% is represented;
(d) the food wastewater FW2 that dilution volume is 2% is represented.
Fig. 2 is FW and three difference COs of the S.obliquus in different diluted concentrations2Total nitrogen (TN) under concentration level Removal rate:
(a) undiluted secondary urban sewage MWW is represented;
(b) the food wastewater FW0.5 that dilution volume is 0.5% is represented:
(c) the food wastewater FW1 that dilution volume is 1% is represented;
(d) the food wastewater FW2 that dilution volume is 2% is represented.
Fig. 3 is FW and three difference COs of the S.obliquus in different diluted concentrations2Total phosphorus (TP) under concentration level Removal rate:
(a) undiluted secondary urban sewage MWW is represented;
(b) the food wastewater FW0.5 that dilution volume is 0.5% is represented:
(c) the food wastewater FW1 that dilution volume is 1% is represented;
(d) the food wastewater FW2 that dilution volume is 2% is represented.
Fig. 4 is FW and three difference COs of the S.obliquus in different diluted concentrations2Fatty acid methyl ester under concentration level (FAME) composition, wherein SFA represent saturated fatty acid, and MUFA represents monounsaturated fatty acids, and PUFA represents how unsaturated fat Fat acid:
(a) undiluted secondary urban sewage MWW is represented;
(b) the food wastewater FW0.5 that dilution volume is 0.5% is represented;
(c) the food wastewater FW1 that dilution volume is 1% is represented;
(d) the food wastewater FW2 that dilution volume is 2% is represented
Fig. 5 is FW and three difference COs of the S.obliquus in different diluted concentrations2Carbohydrate under concentration level, The content and productivity of lipid:
(a) undiluted secondary urban sewage MWW is represented;
(b) the food wastewater FW0.5 that dilution volume is 0.5% is represented:
(c) the food wastewater FW1 that dilution volume is 1% is represented;
(d) the food wastewater FW2 that dilution volume is 2% is represented
Specific implementation mode
Below by specific embodiments and the drawings, the present invention is further illustrated.The embodiment of the present invention is in order to more So that those skilled in the art is more fully understood the present invention well, any limitation is not made to the present invention.
Embodiment 1
The typical group of the present embodiment flue gas becomes CO2:14.1%;CO:300ppm;NOX:207ppm;SOX:53ppm
Steps are as follows for the method for the present invention:
1) commercially available scenedesmus S.obliquus is inoculated in 2L cylindrical chambers, wherein the BBM culture mediums containing 1.7L, Inoculation volume is 10% (VInoculum/VCulture medium), it is subsequently placed in light incubator and cultivates 10 days;Condition of culture is 23 DEG C of temperature, white 110 μm of ol.m of fluorescent illumination2.s-1And it is passed through 0.5L.min-1Filtration sterilization air conditions under cultivate, scenedesmus suspension matrix train The absorbance supported in base is adjusted to 0.5.
BBM culture medium groups become shown in following table:
Title Concentration/(mg.L-1) Title Concentration/(mg.L-1)
NaNO3 250 KH2PO4 175
K2HPO4 75 MgSO4·7H2O 75
CaCl2·2H2O 25 NaCl 25
EDTA 50 KOH 31
FeSO4·7H2O 4.98 H3BO3 11.42
ZnSO4·7H2O 8.82 MnCl2 1.44
MoO3 0.71 CuSO4·5H2O 1.57
Co(NO3)2·6H2O 0.49
2) pretreatment of waste water:Secondary urban sewage (MWW) and food wastewater (FW) are removed using 0.2 μm of nylon micro-filtration Microorganism and suspended solid particles, and carry out 121 DEG C of high pressure sterilization processing.
Secondary urban sewage (MWW) is collected from municipal sewage plant, and food wastewater (FW) comes from food wastewater treatment plant.
TN=21 ± the 0.4mg/L, TP=2.3 ± 0.2mg/L, TOC=18.6 ± 0.2mg/ of secondary urban sewage (MWW) L;
TN=725 ± the 1.6mg/L, TP=62.5 ± 1.1mg/L, TOC=10173 ± 2.3mg/L of food wastewater (FW);
3) basic culture experiment:In BBM culture mediums, with 5% CO2Synthesis gas (includes 5%CO2And 95%N2Group Point) S.obliquus scenedesmus is cultivated under following condition of culture 6 days;
Condition of culture:23 DEG C of temperature, white fluorescent illuminate 110 μm of ol.m2.s-1
4) simultaneous foster pattern culture experiment:
A, in 500 milliliters of aluminium means of press seals serum bottles, the secondary urban sewage MWW of 300 milliliters of filtration sterilization processing is added, It is inoculated with 3% (VInoculum/VWaste water), it is aided with food wastewater FW and flue gas CO2
B, MWW filtrates are diluted with FW, and the FW volume dilutions concentration 0.5,1,2% and 3 differences of 3 different levels is arranged Horizontal CO2Concentration 5,10,14.1%;
C, 12 sewage solution are shared:Municipal sewage MWW and diluent FW volume ratios 100:0 (MWW, respectively in 5,10 and 14.1%CO2Under), 99.5:0.5 (FW0.5, in 5,10 and 14.1%CO2Under), 99:1 (FW1, in 5,10 and 14.1% CO2 Under) and 98:2 (FW2, in 5,10 and 14.1% CO2Under);
D, above-mentioned sewage solution is placed in inoculation bottle, is cultivated in 150rpm, 27 DEG C of water bath, white fluorescent illumination Intensity is 120 μm of ol.m2.s-1Culture 6 days.
Embodiment 2
The typical group of the present embodiment flue gas becomes CO2:14.1%;CO:300ppm;NOX:207ppm;SOX:53ppm
Steps are as follows for the method for the present invention:
1) commercially available scenedesmus S.obliquus is inoculated in 2L cylindrical chambers, wherein the BBM culture mediums containing 1.7L, Inoculation volume is 10% (VInoculum/VCulture medium), it is subsequently placed in light incubator and cultivates 15 days;Condition of culture is 27 DEG C of temperature, white 135 μm of ol.m of fluorescent illumination2.s-1And it is passed through 1.0L.min-1Filtration sterilization air conditions under cultivate, scenedesmus suspension matrix train The absorbance supported in base is adjusted to 1.0.
BBM culture mediums are formed with embodiment 1
2) pretreatment of waste water:Secondary urban sewage (MWW) and food wastewater (FW) are removed using 0.2 μm of nylon micro-filtration Microorganism and suspended solid particles, and carry out 100 DEG C of high pressure sterilization processing.
Secondary urban sewage (MWW) is collected from municipal sewage plant, and food wastewater (FW) comes from food wastewater treatment plant.
TN=21 ± the 0.4mg/L, TP=2.3 ± 0.2mg/L, TOC=18.6 ± 0.2mg/ of secondary urban sewage (MWW) L;
TN=725 ± the 1.6mg/L, TP=62.5 ± 1.1mg/L, TOC=10173 ± 2.3mg/L of food wastewater (FW);
3) basic culture experiment:In BBM culture mediums, with 5% CO2Synthesis gas (includes 5%CO2And 95%N2Group Point) S.obliquus scenedesmus is cultivated under following condition of culture 10 days;
Condition of culture:27 DEG C of temperature, white fluorescent illuminate 135 μm of ol.m2.s-1
4) simultaneous foster pattern culture experiment:
A, in 500 milliliters of aluminium means of press seals serum bottles, the secondary urban sewage MWW of 300 milliliters of filtration sterilization processing is added, It is inoculated with 5% (VInoculum/VWaste water), it is aided with food wastewater FW and flue gas CO2
B, MWW filtrates are diluted with FW, and the FW volume dilutions concentration 0.5,1,2% and 3 differences of 3 different levels is arranged Horizontal CO2Concentration 5,10,14.1%;
C, 12 sewage solution are shared:Municipal sewage MWW and diluent FW volume ratios 100:0 (MWW, respectively in 5,10 and 14.1%CO2Under), 99.5:0.5 (FW0.5, in 5,10 and 14.1%CO2Under), 99:1 (FW1, in 5,10 and 14.1% CO2 Under) and 98:2 (FW2, in 5,10 and 14.1% CO2Under);
D, above-mentioned sewage solution is placed in inoculation bottle, is cultivated in 150rpm, 27 DEG C of water bath, white fluorescent illumination Intensity is 120 μm of ol.m2.s-1Culture 6 days.
Embodiment 3
The typical group of the present embodiment flue gas becomes CO2:14.1%;CO:300ppm;NOX:207ppm;SOX:53ppm
Steps are as follows for the method for the present invention:
1) commercially available scenedesmus S.obliquus is inoculated in 2L cylindrical chambers, wherein the BBM culture mediums containing 1.7L, Inoculation volume is 10% (VInoculum/VCulture medium), it is subsequently placed in light incubator and cultivates 13 days;Condition of culture is 25 DEG C of temperature, white 125 μm of ol.m of fluorescent illumination2.s-1And it is passed through 0.75L.min-1Filtration sterilization air conditions under cultivate, scenedesmus suspension is in matrix Absorbance in culture medium is adjusted to 0.8.
BBM culture mediums are formed with embodiment 1
2) pretreatment of waste water:Secondary urban sewage (MWW) and food wastewater (FW) are removed using 0.2 μm of nylon micro-filtration Microorganism and suspended solid particles, and carry out 115 DEG C of high pressure sterilization processing.
Secondary urban sewage (MWW) is collected from municipal sewage plant, and food wastewater (FW) comes from food wastewater treatment plant.
TN=21 ± the 0.4mg/L, TP=2.3 ± 0.2mg/L, TOC=18.6 ± 0.2mg/ of secondary urban sewage (MWW) L;
TN=725 ± the 1.6mg/L, TP=62.5 ± 1.1mg/L, TOC=10173 ± 2.3mg/L of food wastewater (FW);
3) basic culture experiment:In BBM culture mediums, with 5% CO2Synthesis gas (includes 5%CO2And 95%N2Group Point) S.obliquus scenedesmus is cultivated under following condition of culture 8 days;
Condition of culture:25 DEG C of temperature, white fluorescent illuminate 125 μm of ol.m2.s-1
4) simultaneous foster pattern culture experiment:
A, in 500 milliliters of aluminium means of press seals serum bottles, the secondary urban sewage MWW of 300 milliliters of filtration sterilization processing is added, It is inoculated with 4% (VInoculum/VWaste water), it is aided with food wastewater FW and flue gas CO2
B, MWW filtrates are diluted with FW, and the FW volume dilutions concentration 0.5,1,2% and 3 differences of 3 different levels is arranged Horizontal CO2Concentration 5,10,14.1%;
C, 12 sewage solution are shared:Municipal sewage MWW and diluent FW volume ratios 100:0 (MWW, respectively in 5,10 and 14.1%CO2Under), 99.5:0.5 (FW0.5, in 5,10 and 14.1%CO2Under), 99:1 (FW1, in 5,10 and 14.1%CO2Under) With 98:2 (FW2, in 5,10 and 14.1% CO2Under);
D, above-mentioned sewage solution is placed in inoculation bottle, is cultivated in 150rpm, 27 DEG C of water bath, white fluorescent illumination Intensity is 120 μm of ol.m2.s-1Culture 6 days.
Fig. 1 is FW and three difference COs of the S.obliquus in different diluted concentrations2Schematic diagram is grown under concentration level;
Fig. 2 is FW and three difference COs of the S.obliquus in different diluted concentrations2Total nitrogen (TN) under concentration level Removal rate;
Fig. 3 is FW and three difference COs of the S.obliquus in different diluted concentrations2Total phosphorus (TP) under concentration level Removal rate;
Fig. 4 is FW and three difference COs of the S.obliquus in different diluted concentrations2Fatty acid methyl ester under concentration level (FAME) composition, wherein SFA represent saturated fatty acid, and MUFA represents monounsaturated fatty acids, and PUFA represents how unsaturated fat Fat acid;
By Fig. 1 to Fig. 4 it can be seen that being aided with food wastewater FW and being passed through C02The simultaneous foster pattern condition of culture of gas Under, be conducive to the growth of scenedesmus.Wherein, the food wastewater FW0.5 and FW1.0 that scenedesmus is 0.5% and 1% in dilution volume The middle CO cultivated and be passed through 10% and 14.1%2Growing state is best after gas.And foster pattern culture scenedesmus is for TN nutrition Removal effect is preferable, food wastewater FW0.5 and FW1.0 and be passed through 10% and 14.1% CO2Gas culture can reach highest TN remove 21-22mg.L-1, and it is relatively low that scenedesmus removal TN is cultivated in MWW and FW2.Scenedesmus exists for the removal of TP It is not much different under each condition of culture, can obtains preferable removal effect.In food wastewater FW0.5 and FW1.0 and it is passed through 10% and 14.1% CO2Scenedesmus can reach highest lipid production rate 10-11mg.L under gas condition of culture-1.d-1And carbon water Production of chemicals rate 13-16mg.L-1.d-1.Meanwhile food wastewater is respectively by the aliphatic acid in scenedesmus, palmitic acid and oleic acid content It is increased to 8% and 6%.Utilize food wastewater and CO2The simultaneous foster pattern of flue gas is conducive to the culture of scenedesmus, obtains higher Lipid and carbohydrate productivity also achieve the purified treatment of waste water simultaneously.
It should be understood that embodiment and example discussed herein simply to illustrate that, to those skilled in the art For, it can be improved or converted, and all these modifications and variations should all belong to the protection of appended claims of the present invention Range.
Pertinent literature:
[1].Bhatnagar,A.,Chinnasamy,S.,Singh,M.,Das,K.C.,2011.Renewable biomass production by mixotrophic algae in the presence of various carbon sources and wastewaters.Appl.Energ.88, 3425-3431.
[2].Lizzul,A.M.,Hellier,P.,Purton,S.,Baganz,F.,Ladommatos,N.,Campos, L.,2014.Combined remediation and lipid production using Chlorella sorokiniana grown on wastewater and exhaust gases.Bioresour.Technol.151,12-18.
[3].Chiu,S.Y.,Kao,C.Y.,Huang,T.T.,Lin,C.J.,Ong,S.C.,Chen,C.D.,Chang, J.S.,Lin, C.S.,2011.Microalgal biomass production and on-site bioremediation of carbon dioxide,nitrogen oxide and sulfur dioxide from flue gas using Chlorella sp.cultures.Bioresour.Technol.102, 9135-9142.
[4].Salama,E.-S.,Kabra,A.N.,Ji,M.-K.,Kim,J.R.,Min,B.,Jeon,B.-H., 2014.Enhancement of microalgae growth and fatty acid content under the influence of phytohormones.Bioresour.Technol. 172,97-103.
[5].Cohen,Y.,Kirchmann,H.,2004.Increasing the pH of wastewater to high levels with different gases-CO2 stripping.Water Air Soil Poll.159,265- 275.
[6].Zhang,L.,Jahng,D.,2010.Enhanced anaerobic digestion of piggery wastewater by ammonia stripping:effects of alkali types.J.Hazard.Mater.182, 536-543.
[7].Hu,B.,Min,M.,Zhou,W.,Du,Z.,Mohr,M.,Chen,P.,Zhu,J.,Cheng,Y.,Liu, Y.,Ruan, R.,2012.Enhanced mixotrophic growth of microalga Chlorella sp.on pretreated swine manure for simultaneous biofuel feedstock production and nutrient removal.Bioresour.Technol.126,71-79.

Claims (3)

1. a kind of research method of simultaneous foster pattern scenedesmus culture for waste water fume treatment, which is characterized in that including walking as follows Suddenly:
1) scenedesmus is inoculated with:Scenedesmus S.obliquus is inoculated in container, BBM culture mediums are added, inoculation volume is that 10% (V connects Kind object/V culture mediums), it is subsequently placed in light incubator and cultivates 10~15 days;
Condition of culture is:23~27 DEG C of temperature, white fluorescent illuminate 110~135 μm of ol.m2.s-1And it is passed through 0.5~1.0L.min-1Filtration sterilization air conditions under cultivate, absorbance of the scenedesmus suspension in matrix culture medium is adjusted to 0.5~1.0;
2) Wastewater Pretreatment:Micro-filtration removes microorganism and suspended solid particles in waste water, and carries out 100~121 DEG C of high pressure sterilizations Processing;
Wherein, waste water comes from secondary urban sewage and food wastewater;
3) basic culture experiment:In BBM culture mediums, with 5% CO2Synthesis gas is cultivated under following condition of culture S.obliquus scenedesmus 6~10 days;
Condition of culture:23~27 DEG C of temperature, white fluorescent illuminate 110~135 μm of ol.m2.s-1
4) simultaneous foster pattern culture experiment:
(1) in aluminium means of press seals serum bottle, 300 milliliters of above-mentioned steps 2 are added) in sterilized processing secondary urban sewage, connect 3~5% (V of kindInoculum/VWaste water), it is aided with food wastewater and flue gas CO2
(2) secondary urban sewage filtrate is diluted with food wastewater, and the food wastewater volume dilution that 3 different levels are arranged is a concentration of 0.5, the CO of 1,2% and 3 different levels2A concentration of 5,10,14.1%;
(3) 12 sewage solution are prepared altogether:Secondary urban sewage and food wastewater volume ratio are 100:0 (secondary urban sewage, point Not in 5,10 and 14.1%CO2Under), 99.5:0.5 (food wastewater 0.5, in 5,10 and 14.1%CO2Under), 99:1 (food wastewater 1, in 5,10 and 14.1%CO2Under) and 98:2 (food wastewaters 2, in 5,10 and 14.1% CO2Under);
(5) the sewage solution is placed in inoculation bottle, is cultivated in 150rpm, 27 DEG C of water bath, white fluorescent illumination is strong Degree is 120 μm of ol.m2.s-1Culture 6 days.
2. a kind of research method of simultaneous foster pattern scenedesmus culture for waste water fume treatment according to claim 1, It is characterized in that, micro-filtration uses 0.2 μm of nylon in the step 2).
3. a kind of research method of simultaneous foster pattern scenedesmus culture for waste water fume treatment according to claim 1, It is characterized in that, CO in the step 3)2Synthesis gas is by 5%CO2And 95%N2Composition.
CN201810340119.1A 2018-04-16 2018-04-16 A kind of research method of simultaneous foster pattern scenedesmus culture for waste water fume treatment Pending CN108424857A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810340119.1A CN108424857A (en) 2018-04-16 2018-04-16 A kind of research method of simultaneous foster pattern scenedesmus culture for waste water fume treatment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810340119.1A CN108424857A (en) 2018-04-16 2018-04-16 A kind of research method of simultaneous foster pattern scenedesmus culture for waste water fume treatment

Publications (1)

Publication Number Publication Date
CN108424857A true CN108424857A (en) 2018-08-21

Family

ID=63161212

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810340119.1A Pending CN108424857A (en) 2018-04-16 2018-04-16 A kind of research method of simultaneous foster pattern scenedesmus culture for waste water fume treatment

Country Status (1)

Country Link
CN (1) CN108424857A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109456895A (en) * 2018-10-23 2019-03-12 天津大学 A kind of CO that chemical absorbing is coupled with bioconversion2Capture method
CN109609383A (en) * 2018-12-11 2019-04-12 天津大学 Regulate and control and utilize NH based on pH4HCO3The microalgae culture method of absorbing liquid
CN109897784A (en) * 2019-02-27 2019-06-18 天津大学 A kind of method that novel two stages autotrophy-Heterotrophic culture promotes microalgae lipid

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102250773A (en) * 2011-05-31 2011-11-23 中国科学院青岛生物能源与过程研究所 Scenedesmus as well as culturing method and application thereof
CN104593264A (en) * 2015-01-29 2015-05-06 山东大学 High-oil-yield scenedesmus SDEC-13 and culture method and application thereof
CN106399109A (en) * 2016-11-07 2017-02-15 辽宁东科电力有限公司 Chlorella vulgaris used for combined treatment of wastewater and waste gas while synchronously realizing solid carbon denitrification
CN106434353A (en) * 2016-11-21 2017-02-22 九江学院 Microalgae culturing method and application thereof
CN107760605A (en) * 2017-11-27 2018-03-06 天津大学 A kind of research method that tofu wastewater is purified using microdisk electrode

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102250773A (en) * 2011-05-31 2011-11-23 中国科学院青岛生物能源与过程研究所 Scenedesmus as well as culturing method and application thereof
CN104593264A (en) * 2015-01-29 2015-05-06 山东大学 High-oil-yield scenedesmus SDEC-13 and culture method and application thereof
CN106399109A (en) * 2016-11-07 2017-02-15 辽宁东科电力有限公司 Chlorella vulgaris used for combined treatment of wastewater and waste gas while synchronously realizing solid carbon denitrification
CN106434353A (en) * 2016-11-21 2017-02-22 九江学院 Microalgae culturing method and application thereof
CN107760605A (en) * 2017-11-27 2018-03-06 天津大学 A kind of research method that tofu wastewater is purified using microdisk electrode

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
A.M. LIZZUL ET AL.,: ""Combined remediation and lipid production using Chlorella sorokiniana grown on wastewater and exhaust gases"", 《BIORESOURCE TECHNOLOGY》 *
ASHISH BHATNAGAR ET AL.,: ""{Renewable biomass production by mixotrophic algae in the presence of various carbon sources and wastewaters"", 《APPLIED ENERGY》 *
姚丽丽: ""混合废水耦合CO2培养微藻及处理废水的研究"", 《中国优秀硕士学位论文全文数据库工程科技Ⅰ辑》 *
赵桂丽: ""不同碳源及培养方法对栅藻生产油脂的影响"", 《中国优秀硕士学位论文全文数据库 基础科学辑》 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109456895A (en) * 2018-10-23 2019-03-12 天津大学 A kind of CO that chemical absorbing is coupled with bioconversion2Capture method
CN109609383A (en) * 2018-12-11 2019-04-12 天津大学 Regulate and control and utilize NH based on pH4HCO3The microalgae culture method of absorbing liquid
CN109897784A (en) * 2019-02-27 2019-06-18 天津大学 A kind of method that novel two stages autotrophy-Heterotrophic culture promotes microalgae lipid

Similar Documents

Publication Publication Date Title
Wu et al. Lipid accumulating microalgae cultivation in textile wastewater: Environmental parameters optimization
Ji et al. Mixotrophic cultivation of a microalga Scenedesmus obliquus in municipal wastewater supplemented with food wastewater and flue gas CO2 for biomass production
Ji et al. Biomass production and nutrients removal by a new microalgae strain Desmodesmus sp. in anaerobic digestion wastewater
Shen et al. Effect of carbon source on biomass growth and nutrients removal of Scenedesmus obliquus for wastewater advanced treatment and lipid production
Jiang et al. Utilization of simulated flue gas for cultivation of Scenedesmus dimorphus
Ji et al. Removal of nitrogen and phosphorus from piggery wastewater effluent using the green microalga Scenedesmus obliquus
Choi et al. Microalgal biomass and lipid production on dairy effluent using a novel microalga, Chlorella sp. isolated from dairy wastewater
Praveen et al. Photosynthetic aeration in biological wastewater treatment using immobilized microalgae-bacteria symbiosis
CN105712490B (en) A kind of method of mixotroph nutrition conversion processing high ammonia-nitrogen wastewater
Wang et al. Performance of different microalgae-based technologies in biogas slurry nutrient removal and biogas upgrading in response to various initial CO2 concentration and mixed light-emitting diode light wavelength treatments
Jiang et al. Biomass production and nutrient assimilation by a novel microalga, Monoraphidium spp. SDEC-17, cultivated in a high-ammonia wastewater
Ouyang et al. Effect of light intensity on the capability of different microalgae species for simultaneous biogas upgrading and biogas slurry nutrient reduction
Koutra et al. Microalgal post-treatment of anaerobically digested agro-industrial wastes for nutrient removal and lipids production
Yan et al. Influence of influent methane concentration on biogas upgrading and biogas slurry purification under various LED (light-emitting diode) light wavelengths using Chlorella sp.
Wu et al. Textile wastewater bioremediation using immobilized Chlorella sp. Wu-G23 with continuous culture
CN108424857A (en) A kind of research method of simultaneous foster pattern scenedesmus culture for waste water fume treatment
Zhang et al. Removal of pollutants from biogas slurry and CO 2 capture in biogas by microalgae-based technology: a systematic review
CN111808754A (en) Mining area soil microalgae and separation and purification method and application thereof
Liu et al. Growth and nutrient utilization of green algae in batch and semicontinuous autotrophic cultivation under high CO 2 concentration
Xie et al. Blending high concentration of anaerobic digestion effluent and rainwater for cost-effective Chlorella vulgaris cultivation in the photobioreactor
Zhang et al. Ammonia-nitrogen and orthophosphate removal by immobilized Chlorella sp. isolated from municipal wastewater for potential use in tertiary treatment
CN105776745A (en) Biological treatment method of high-ammonia nitrogen pig raising biogas slurry
TW201336986A (en) Biogas electric generator and electricity generation method using microalgae carbon capture
Patidar et al. Effect of carbon supply mode on biomass and lipid in CSMCRI's Chlorella variabilis (ATCC 12198)
Tan et al. Anaerobic digestates grown oleaginous microalgae for pollutants removal and lipids production

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
WD01 Invention patent application deemed withdrawn after publication
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20180821