CN108220202A - A kind of method that biogas biologic recycling utilizes - Google Patents

A kind of method that biogas biologic recycling utilizes Download PDF

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CN108220202A
CN108220202A CN201810169103.9A CN201810169103A CN108220202A CN 108220202 A CN108220202 A CN 108220202A CN 201810169103 A CN201810169103 A CN 201810169103A CN 108220202 A CN108220202 A CN 108220202A
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biogas
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methylobacterium
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费强
傅容湛
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Xian Jiaotong University
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Abstract

The present invention discloses a kind of method that biogas biologic recycling utilizes, and can pass through High Density Cultivation aerobic methane backeria aerobic methane backeria synthesising biological matter and the other-end product of continuously ventilating using biogas as fermentation substrate using this method.Present invention can apply to the extensive high efficiency productions of aerobic methane backeria and its active material.By optimizing aerobic methane backeria condition of culture and medium component, the bioavailable efficiency of biogas is improved, so as to make 20 40g/L of organism dry weight concentration, dry cell weight yield 10 20g/L/ days that biogas biosynthesis obtains, 2 10g/L of production concentration.Biological utilisation for biogas provides a kind of method of high-efficiency resource recycling.

Description

A kind of method that biogas biologic recycling utilizes
Technical field
The present invention relates to a kind of methods by bioanalysis recycling biogas, belong to biological chemical field.
Background technology
In recent years, the change for resulting in environment is significantly increased in firedamp drainage amount, is brought for the mankind and other species huge Big harm.Research shows that the growth of demographic and economic increases the consumption to the energy, it is contemplated that the middle of this century, consumption By at least current twice.Currently, existing lot of research shows that fossil energy consumption, firedamp drainage and global environment become Relationship between change, correlated results point out that environmental change influences not allowing to neglect caused by society and economic dispatch various aspects simultaneously Depending on.
Biogas mainly includes the carbon dioxide and methane based on one gas of carbon.Research shows that cause the natural pond of global warming In gas, the proportion of methane has reached 20%, and is calculated with 20 terms, and the global warming potential of methane is 86 times of carbon dioxide. Methane derives from a wealth of sources, and garbage loading embeading factory, sewage treatment plant, animal farm etc. are mainly present in the form of biogas can carry out micro- life Object anaerobic degradation fermentation place.
China attaches great importance to Methane Resources in recent years, and with its production technology constantly improve, biogas has become a kind of honest and clean Valency, sufficient carbon source.But the current a large amount of biogas utilizations in China are mainly burnt based on still being utilized with low-grade heat by cogeneration of heat and power Methane in biogas generates thermal energy and electric energy.However this inefficient method using biogas, not only greatly reduce the valency of biogas Value, and the carbon dioxide that combustion of methane generates causes secondary pollution.Therefore being continuously increased with biogas output, biogas High-end utilization ways are badly in need of constantly extension and supplement.
Aerobic methane backeria is a kind of microorganism that can be using methane as sole carbon source and energy source, distinctive in vivo Biogas can be biologically converted into including microbial grease, long chain fatty acids, glycogen, poly-β-hydroxybutyric acid, extracellular polymer by biological enzyme A variety of high value active materials including object, tetrahydropyrimidine, epoxides, astaxanthin, methanol, mycoprotein etc..Therefore, mesh Preceding aerobic methane backeria has a wide range of applications in food, medicine, feed, all various aspects such as environmental protection and bioenergy.
But aerobic methane backeria requires condition of culture extremely harsh.Not optimised growth conditions and condition of culture be difficult Realize that the methane in aerobic methane backeria Efficient Conversion biogas generates the purpose of high value added product.It is compared to and is using carbohydrate The microorganism of carbon substrate, the sole carbon source and energy source of aerobic methane backeria are biogas.Gaseous carbon sources have relative to carbohydrate It is not easy to be controlled and the characteristics of transformation efficiency is low.It can not such as be realized without the optimization of condition of culture and efficiently realize height using biogas The purpose of density fermentation, so as to lose the prospect of industrialized production.
Invention content
The present invention for current Methane Resourcesization using technology existing during insufficient and bioconversion methane and The jejune problem of condition by optimizing aerobic methane backeria condition of culture and medium component, improves the utilization ratio of biogas.
Culture aerobic methane backeria is carried out using the training method continuously ventilated, biogas is continuously passed through simultaneously in incubation Exclusive segment bacterium solution, while the Optimal Medium for adding respective volume carries out subsequent technology culture.
The aerobic methane backeria is selected from:Methylomonas pelagica,Pseudomonas methanica, Methylosinus trichosporium OB3b,Methylosinus sporium,Methylobacter modestohalophilus,Methylocystis parvus,Methylomicrobium specie,Methylomonas methanica,Methylomonas albus,Methylobacter alcaliphilus,Methylococcus capsulatus(Bath),Methylobacter album,Methylobacterium extorquens, Methylobacter capsulatus,Methylobacterium organophilum,Methylomonas specie, Methylomicrobium buryatense,Methylomicrobium alcaliphilum,Methylobacterium radiotolerans,Methylocella silvestris,Methylobacterium populi, Methylacidiphilum infernorum,Methylibium petroleiphilum,Methylocystis GB25, Methylobacterium chloromethanicum,Verrucomicrobia phylum,Methylobacterium The compound mixed bacterial of nodulans, Methylomicrobium alcaliphilum or above-mentioned strain.
The aerobic methane backeria in culture of continuous cultivation, controls bioreactor using biogas as sole carbon source Speed of agitator is 200-1000 revs/min, and biogas is continuously passed through bioreactor with the flow of 0.5-3vvm, and keep cultivating Temperature is 20-35 DEG C, and the pH for adjusting culture solution in culture medium and bioreactor is 5.0-10.0.
The culture medium is made of nitrogen source, carbonate, inorganic salts, trace element and water
The continuous culture is in revolving bottle, mechanical agitation type, gas-lifting type, bubble type or the circulating biological respinse of biomembrane It is carried out in device.
The biomass and other-end product include drying thalline, microbial grease, mycoprotein, glycogen and poly- β- Hydroxybutyric acid.
The main component of the liquid medium is:MgSO4·7H20.2~5.0 g/l of O, CaCl2·6H2O0.002~ 0.2 g/l, KNO30.1-10.0 g/l, NaNO30.5-5.0 g/l, K2SO40.1-1.0 g/l, NaCl 1.0- 10.0 g/l, KH2PO40.1~1.0 g/l, Na2HPO40.1~1.0 g/l, NaHCO30.5-5.0 g/l, Na2CO3 1.0-5.0 g/l, 0.5~5 g/l of Na-EDTA, FeSO4·7H20.1~4 g/l of O, ZnSO47H2O 0.01~1.2 G/l, MnSO4·4H2O 0.1-0.5 g/l, MnCl2·4H20.003~0.1 g/l of O, H3BO30.02~0.12 gram/ It rises, CoCl2·6H2O0.02~0.4 g/l, CuCl2·2H2O 0.02-0.6 g/l, CaCl2·2H2O 0.001-0/1 gram/ It rises, NiCl2·6H20.002~0.1 g/l of O, Na2MoO4·2H20.003~0.1 g/l of O, CuSO4·5H2O0.5~5 G/l, 0.05-1.0 g/l of KI (potassium iodide) and 1mM H2SO40.1-2ml, the composition of chelant ferrous solution is FeSO4·7H2O 0.5-10.0 g/l, FeCl31.0-5.0 g/l, HCl 1.0-5.0ml and Na2- EDTA 0.5-4.0 g/l are realized highly dense The degree continuous culture aerobic methane backeria.
The biomass dry weight that the aerobic methane backeria obtains after high density is continuously cultivated reaches 20-40g/L.
For the present invention by optimizing aerobic methane backeria condition of culture and medium component, that improves methane in sewage gas utilizes effect Rate, so as to make organism dry weight concentration 20-40g/L, the dry cell weight yield 10-20g/L/ days, product that methane biosynthesis obtains Concentration 2-10g/L.Utilization for biogas provides a kind of method of high-performance bio method recycling.
Description of the drawings
Fig. 1 is embodiment 1, biomass growth rate curve graph in example 2 and example 3.Each component meaning in Fig. 1:#A, #B and #C Represent above-mentioned three kinds of different culture medias;OD represents thalline absorbance value;Time represents the time hour (h).
Fig. 2 is embodiment 1, cell dry weight concentration curve graph in example 2 and example 3.Each component meaning in Fig. 2:#A, #B and #C Represent above-mentioned three kinds of different culture medias;DCW represents cell dry weight concentration gram per liter (g/L) in figure;Time represents the time hour (h)。
Fig. 3 is embodiment 1, bio-oil content curve graph in example 2 and example 3.Each component meaning in Fig. 3:#A, #B and #C Represent above-mentioned three kinds of different culture medias;Lipid content represent the ratio that bio-oil (i.e. product) accounts for dry cell weight;Time Represent the time hour (h).
Fig. 4 is biomass growth rate, cell dry weight concentration and glycogen concentration curve graph in embodiment 4.Each component in Fig. 4 Meaning:;OD represents thalline absorbance value;DCW represents cell dry weight concentration gram per liter (g/L);Glycogen represents glycogen concentration Gram per liter (g/L);Time represents the time hour (h).
Specific embodiment
The present invention is described in further detail below by specific embodiment, but the aerobic methane backeria of the present patent application Including but not limited to Methylomonas pelagica, Pseudomonas methanica, Methylosinus trichosporium OB3b,Methylosinus sporium,Methylobacter modestohalophilus, Methylocystis parvus,Methylomicrobium specie,Methylomonas methanica, Methylomonas albus,Methylobacter alcaliphilus,Methylococcus capsulatus(Bath), Methylobacter album,Methylobacterium extorquens,Methylobacter capsulatus, Methylobacterium organophilum,Methylomonas specie,Methylomicrobium buryatense,Methylomicrobium alcaliphilum,Methylobacterium radiotolerans, Methylocella silvestris,Methylobacterium populi,Methylacidiphilum infernorum, Methylibium petroleiphilum,Methylocystis GB25,Methylobacterium chloromethanicum,Verrucomicrobia phylum,Methylobacterium nodulans, The compound mixed bacterial of Methylomicrobium alcaliphilum or above-mentioned strain.
In a preferred embodiment, the present invention uses Methylomicrobium buryatense, For Methylomicrobium alcaliphilum, Methylosinus trichosporium OB3b mixed bacterials, say The specific embodiment of the bright present invention.In the case of without prejudice to spirit of the invention and essence, to the method for the present invention, step or item The modifications or substitutions that part is made, all belong to the scope of the present invention.
Embodiment 1:
Prepare liquid medium #A and liquid microelement #1 (its composition is shown in Tables 1 and 2), by the liquid medium accordingly prepared with Liquid microelement is added in bioreactor, and to working volume, the Liquid Fill coefficient of bioreactor is supplement pure water 0.6.The continuous culture of mixed bacterial carries out in the bioreactor of revolving bottle, mechanical agitation type, gas-lifting type or bubble type. In preferred example, using mechanical agitation type bioreactor.
Steam sterilizing is carried out to the bioreactor for having filled liquid (121 DEG C maintain 30 minutes).When temperature is down to 30 DEG C, press 8% access seed liquor of dress liquid product starts continuously to cultivate.
In incubation, suitable condition of culture must be controlled to realize the High Density Cultivation of mixed bacterial.Preferred real In example, control 500 revs/min of speed of agitator and biogas is passed through with the flow of 0.8vvm, oxyty is kept to be more than 10% as possible. Controlled at 28 DEG C, using 4mol/L NaOH and 4mol/L H2SO4It is 9.0 to regulate and control pH.
After continuous culture starts, liquid medium #A and liquid microelement #1 can realize High Density Cultivation.OD peaks reach 48.5 (see Fig. 1), cell dry weight concentration reach 19.4g/L (see Fig. 2), and product fat content is 11% (see Fig. 3).
Embodiment 2
Described in Tables 1 and 2, liquid medium #B and liquid microelement #2, other condition of culture and patent requirements are prepared With example 1.
After continuous culture starts, liquid medium #B and liquid microelement #2 provide OD peaks up to 9.6 (see Fig. 1), cell Dry weight concentrations reach 3.9g/L (see Fig. 2), and product fat content is 8% (see Fig. 3).
Embodiment 3
Described in Tables 1 and 2, liquid medium #C and liquid microelement #3, other condition of culture and patent requirements are prepared With example 1.
After continuous culture starts, liquid medium #C and liquid microelement #3 can realize High Density Cultivation.OD peaks are big 52.7 (see Fig. 1), cell dry weight concentration reach 21.1g/L (see Fig. 2), and product fat content is 15% (see Fig. 3).
Embodiment 4:
Prepare liquid medium #C and liquid microelement #2 (its composition is shown in Tables 1 and 2), by the liquid medium accordingly prepared with Liquid microelement is added in bioreactor, and to working volume, the Liquid Fill coefficient of bioreactor is supplement pure water 0.4.The continuous culture of mixed bacterial carries out in the bioreactor of revolving bottle, mechanical agitation type, gas-lifting type or bubble type. In preferred example, using mechanical agitation type bioreactor.
Steam sterilizing is carried out to the bioreactor for having filled liquid (121 DEG C maintain 30 minutes).When temperature is down to 30 DEG C, press 10% access seed liquor of dress liquid product starts continuously to cultivate.
In incubation, suitable condition of culture must be controlled to realize the High Density Cultivation of mixed bacterial.Preferred real In example, control 1000 revs/min of speed of agitator and biogas is passed through with the flow of 2vvm, oxyty is kept to be more than 5% as possible.Control Temperature processed is 30 DEG C, using 2mol/L NaOH and 2mol/L H2SO4It is 8 to regulate and control pH.
After continuous culture starts, liquid medium #A and liquid microelement #3 can realize High Density Cultivation biosynthesis sugar It is former.OD peaks reach 25g/L (see Fig. 4), glycogen concentration 10g/L up to 62 (see Fig. 4), cell dry weight concentration (see Fig. 4).
1 liquid medium constituent of table
2 trace element solution constituent of table
From above-described embodiment as can be seen that by optimizing aerobic methane backeria condition of culture and medium component, natural pond is improved The utilization ratio of methane in gas, so as to which the organism dry weight concentration that biogas biosynthesis obtains be made to be produced not less than 20g/L, dry cell weight Rate was not less than 2g/L not less than 10g/L/ days, production concentration.Utilization for biogas provides a kind of high-performance bio method recycling Method.

Claims (7)

1. a kind of method that biogas biologic recycling utilizes, which is characterized in that by the use of aerobic methane backeria using biogas as uniquely Carbon source catalyzes and synthesizes biogas for biomass and other-end product under high-density culturing condition, in culture of continuous cultivation, The speed of agitator for controlling bioreactor is 200-1200 revs/min, will be continuously passed through with the flow of 0.5-3vvm containing biogas Bioreactor, and it is 20-35 DEG C to keep cultivation temperature, and the pH for adjusting culture solution in culture medium and bioreactor is 5.0- 10.0。
2. the method that a kind of biogas biologic recycling according to claim 1 utilizes, which is characterized in that the aerobic first Alkane bacterium is selected from:Methylomonas pelagica,Pseudomonas methanica,Methylosinus trichosporium OB3b,Methylosinus sporium,Methylobacter modestohalophilus, Methylocystis parvus,Methylomicrobium specie,Methylomonas methanica, Methylomonas albus,Methylobacter alcaliphilus,Methylococcus capsulatus(Bath), Methylobacter album,Methylobacterium extorquens,Methylobacter capsulatus, Methylobacterium organophilum,Methylomonas specie,Methylomicrobium buryatense,Methylomicrobium alcaliphilum,Methylobacterium radiotolerans, Methylocella silvestris,Methylobacterium populi,Methylacidiphilum infernorum, Methylibium petroleiphilum,Methylocystis GB25,Methylobacterium chloromethanicum,Verrucomicrobia phylum,Methylobacterium nodulans, The compound mixed bacterial of Methylomicrobium alcaliphilum or above-mentioned strain.
3. the method that a kind of biogas biologic recycling according to claim 1 utilizes, which is characterized in that the biomass and Other-end product includes drying thalline, microbial grease, mycoprotein, glycogen and poly-β-hydroxybutyric acid.
4. the method that a kind of biogas biologic recycling according to claim 1 utilizes, which is characterized in that High Density Cultivation mistake Journey is that the High Density Cultivation of aerobic methane backeria is carried out using the training method continuously ventilated, and natural pond is continuously passed through in incubation Gas simultaneously excludes part bacterium solution in bioreactor, while the liquid medium realization for adding respective volume subsequently continues to cultivate.
5. the method that a kind of biogas biologic recycling according to claim 1 utilizes, which is characterized in that the continuous culture It is carried out in revolving bottle, mechanical agitation type, gas-lifting type, bubble type or the circulating bioreactor of biomembrane.
6. the method that a kind of biogas biologic recycling according to claim 1 utilizes, which is characterized in that the culture medium by Nitrogen source, carbonate, inorganic salts, trace element and water composition.
7. the method that a kind of biogas biologic recycling according to claim 1 utilizes, it is characterised in that the master of liquid medium It forms and is:MgSO4·7H20.2~5.0 g/l of O, CaCl2·6H20.002~0.2 g/l of O, KNO30.1-10.0 grams/ It rises, NaNO30.5-5.0 g/l, K2SO40.1-1.0 g/l, NaCl 1.0-10.0 g/l, KH2PO40.1~1.0 gram/ It rises, Na2HPO40.1~1.0 g/l, NaHCO30.5-5.0 g/l, Na2CO31.0-5.0 g/l, Na2- EDTA 0.5~ 5 g/l, FeSO4·7H20.1~4 g/l of O, ZnSO4·7H20.01~1.2 g/l of O, MnSO4·4H2O 0.1-0.5 G/l, MnCl2·4H20.003~0.1 g/l of O, H3BO30.02~0.12 g/l, CoCl2·6H2O 0.02~0.4 G/l, CuCl2·2H2O 0.02-0.6 g/l, CaCl2·2H2O 0.001-0/1 g/l, NiCl2·6H2O 0.002~ 0.1 g/l, Na2MoO4·2H20.003~0.1 g/l of O, CuSO4·5H20.5~5 g/l of O, KI (potassium iodide) 0.05- 1.0 g/l and 1mM H2SO40.1-2ml, the composition of chelant ferrous solution is FeSO4·7H2O 0.5-10.0 g/l, FeCl3 1.0-5.0 g/l, HCl 1.0-5.0ml and Na2- EDTA 0.5-4.0 g/l, it is good described in the continuous culture of high density to realize Oxygen methane backeria.
CN201810169103.9A 2018-02-28 2018-02-28 A kind of method that biogas biologic recycling utilizes Pending CN108220202A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113862205A (en) * 2021-05-13 2021-12-31 西安交通大学 Methanotrophic engineering bacterium for producing hydroxyl tetrahydropyrimidine
CN114045235A (en) * 2021-11-04 2022-02-15 西安交通大学 Method for producing single-cell protein and fermentable sugar by using methanotrophic bacteria

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101928731A (en) * 2010-01-19 2010-12-29 中国科学院研究生院 Method for producing methanol by methane bioconversion
US20130071890A1 (en) * 2011-03-15 2013-03-21 Craig S. Criddle Production of PHA using Biogas as Feedstock and Power Source
WO2015058212A1 (en) * 2013-10-18 2015-04-23 Lanzatech New Zealand Limited Microbial conversion of methane

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101928731A (en) * 2010-01-19 2010-12-29 中国科学院研究生院 Method for producing methanol by methane bioconversion
US20130071890A1 (en) * 2011-03-15 2013-03-21 Craig S. Criddle Production of PHA using Biogas as Feedstock and Power Source
WO2015058212A1 (en) * 2013-10-18 2015-04-23 Lanzatech New Zealand Limited Microbial conversion of methane

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
YEON-SUN YOO等: "Comparative Enzyme Inhibitive Methanol Production by Methylosinus Sporium From Simulated Biogas", 《ENVIRONMENTAL TECHNOLOGY》 *
韩北忠主编: "《发酵工程》", 31 January 2013, 中国轻工业出版社 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113862205A (en) * 2021-05-13 2021-12-31 西安交通大学 Methanotrophic engineering bacterium for producing hydroxyl tetrahydropyrimidine
CN113862205B (en) * 2021-05-13 2023-08-01 西安交通大学 Methanotrophic engineering bacteria for producing hydroxy tetrahydropyrimidine
CN114045235A (en) * 2021-11-04 2022-02-15 西安交通大学 Method for producing single-cell protein and fermentable sugar by using methanotrophic bacteria
CN114045235B (en) * 2021-11-04 2022-11-08 西安交通大学 Method for producing single-cell protein and fermentable sugar by using methanotrophic bacteria

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Application publication date: 20180629