WO2023155503A1 - Photosynthetic green algae-based production apparatus for carbon sink algae liquid - Google Patents

Photosynthetic green algae-based production apparatus for carbon sink algae liquid Download PDF

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WO2023155503A1
WO2023155503A1 PCT/CN2022/131687 CN2022131687W WO2023155503A1 WO 2023155503 A1 WO2023155503 A1 WO 2023155503A1 CN 2022131687 W CN2022131687 W CN 2022131687W WO 2023155503 A1 WO2023155503 A1 WO 2023155503A1
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algae
carbon
concentration
algae liquid
sink
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PCT/CN2022/131687
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French (fr)
Chinese (zh)
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李世峰
王康杰
卢群伟
胡蓓娟
王雅凡
秦康曦
王祎
梁盼
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九江地福来农业科技发展有限公司
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    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M21/00Bioreactors or fermenters specially adapted for specific uses
    • C12M21/02Photobioreactors
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G7/00Botany in general
    • A01G7/06Treatment of growing trees or plants, e.g. for preventing decay of wood, for tingeing flowers or wood, for prolonging the life of plants
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M41/00Means for regulation, monitoring, measurement or control, e.g. flow regulation
    • C12M41/06Means for regulation, monitoring, measurement or control, e.g. flow regulation of illumination
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M41/00Means for regulation, monitoring, measurement or control, e.g. flow regulation
    • C12M41/12Means for regulation, monitoring, measurement or control, e.g. flow regulation of temperature
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M41/00Means for regulation, monitoring, measurement or control, e.g. flow regulation
    • C12M41/30Means for regulation, monitoring, measurement or control, e.g. flow regulation of concentration
    • C12M41/36Means for regulation, monitoring, measurement or control, e.g. flow regulation of concentration of biomass, e.g. colony counters or by turbidity measurements
    • 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

Definitions

  • the invention relates to the technical field of carbon sequestration algae liquid production, in particular to a carbon sink algae liquid production equipment, preparation method and application based on photosynthetic green algae.
  • climate change is a major crisis and severe challenge faced by all centuries, and has become a common concern in the fields of international politics, diplomacy, economy and ecology. To deal with climate change, we should pay equal attention to both mitigation and adaptation.
  • climate change mitigation is a long-term and arduous task, while adaptation to climate change is a more realistic and urgent task.
  • Forestry is one of the areas most affected by climate change, and it is also one of the key areas for adapting to climate change identified by my country. Doing a good job in forestry adaptation to climate change is of great significance to enhancing the overall adaptability of the country and maintaining ecological security and climate security.
  • my country's forest resource endowment is insufficient.
  • my country's forest coverage rate is far lower than the global average of 31%.
  • the per capita forest area is only 1/4 of the world's average, and the per capita forest stock is only 1/7 of the world's average.
  • the wetland rate is lower than the global average of 8.6% % of the average level, the per capita wetland area is only 1/5 of the world's per capita, the pressure of wetland protection is great, and the restoration is difficult; the haze is frequent, sandstorms occur frequently, and the task of sand prevention and control is heavy; landscape fragmentation and endangered species are intensified , Biodiversity protection is very urgent.
  • Forests are the largest carbon pool in terrestrial ecosystems, and expanding forest coverage is an important measure to mitigate and respond to climate change that is economically feasible and low-cost in the next 30 to 50 years. Forests have a huge function of sequestering carbon dioxide, which is called "carbon sink”. At the same time, deforestation, forest land degradation, forest fires, pests and diseases, etc., release the stored carbon dioxide into the atmosphere and become a "carbon source”. Taking measures to strengthen the carbon storage and sink functions of forest ecosystems and reduce carbon emissions from forests has become a global consensus and action to deal with climate change, and it has also become one of the goals of China's two commitments to voluntarily reduce emissions. However, the existing carbon sink products are generally only used in forests, and the carbon sink intensity produced is not high.
  • the object of the present invention is to provide a carbon sink algae liquid production equipment, preparation method and application based on photosynthetic green algae, so as to improve the carbon sink intensity.
  • the present invention provides a carbon sequestration algae liquid production equipment based on photosynthetic green algae, including a device cavity, and an algae carbon capture tank disposed in the device cavity;
  • the algae carbon capture tank is connected to the air treatment equipment through the air inlet pipe, connected to the water treatment equipment through the water inlet pipe, and connected to the high-concentration algae liquid storage tank through the algae liquid outlet pipe;
  • the algae carbon capture tank is provided with an algae concentration monitor, a temperature monitor and an algae liquid inlet pipe, and the algae liquid inlet pipe is used to add photosynthetic green algae liquid;
  • the top of the equipment cavity is provided with lighting equipment, and the high-concentration algae liquid storage tank is connected with the filling equipment.
  • the volume of the algae carbon capture tank is not less than 1m 3 .
  • the present invention provides a method for preparing carbon sequestration algae liquid based on photosynthetic green algae, comprising the following steps:
  • Step S10 sending the purified air treated by the air treatment equipment into the algae carbon capture tank, and the purified water treated by the water treatment equipment into the algae carbon capture tank;
  • Step S11 after adding photosynthetic green algae liquid into the algae carbon capture tank, mixing citric acid, CaCl 2 , MgSO 4 7H 2 O, KH 2 PO 4 , CuSO 4 5H 2 O, EDTA-Fe and purified water , into the algae carbon capture tank;
  • Step S12 mixing the pinellia lectin protein after multi-step purification with purified water, and sending it into the algae carbon capture tank;
  • Step S13 setting and maintaining the preset light intensity through the lighting equipment, and setting and maintaining the preset temperature by the temperature monitor;
  • Step S14 carry out continuous cultivation, and maintain the cell concentration of photosynthetic green algae every day through the algae concentration monitor.
  • the cell concentration reaches the preset peak value, discharge the carbon sequestration algae liquid in the algae carbon capture tank into the high concentration algae liquid storage tank middle;
  • Step S15 discharge the carbon sequestration algae liquid in the high-concentration algae liquid storage tank into the filling equipment for filling to form carbon sequestration products.
  • step S12 specifically includes:
  • Step S121 cloning the cloned pinellia lectin gene into a high-expression plasmid with a His tag, and transforming it into a bacterial culture for preliminary culture, and then inducing it with lactose analogue IPTG for secondary culture;
  • Step S122 after high-speed centrifugation of the recultivated bacterial culture to form a cell pellet, the cell pellet is lysed with a lysis buffer of a mixture of Tris, NaCl and protease inhibitors to form a cell lysate;
  • step S123 the cell lysate is sequentially purified by nickel affinity chromatography, ion exchange chromatography column and gel filtration column to obtain Pinellia lectin protein with a preset purity.
  • step S123 specifically includes:
  • the protein was eluted with 500 mM imidazole to form a preliminary eluate;
  • the concentration of citric acid is 20 mg/L
  • the concentration of CaCl 2 is 2 g/L
  • the concentration of MgSO 4 ⁇ 7H 2 O is 2 g/L
  • the concentration of KH 2 PO 4 is 2 g/L
  • L the concentration of CuSO 4 ⁇ 5H 2 O is 2 mg/L
  • the concentration of EDTA-Fe is 20 mg/L.
  • the light intensity is 2800 lux
  • the temperature is 28°C.
  • the preset peak value is 20 million/ml.
  • the carbon sink strength of the carbon sequestration algae liquid increases with the increase of culture time. After reaching the preset peak value, continue to Cultivation will reduce the carbon sink intensity of the carbon sink algae liquid, and the best time to discharge the carbon sink algae liquid and repeat the culture step is 90 days.
  • the application of the carbon sink algae liquid prepared by the above-mentioned carbon sink algae liquid based on photosynthetic green algae preparation method the carbon sink algae liquid is evenly sprayed on the leaf surface of Quercus liaoturgisis, and the carbon sink
  • the concentration of algae sink liquid the stronger the photosynthesis of Quercus liaoturgisis and the increase of carbon sink.
  • the application of the carbon sink algae liquid prepared by the above-mentioned method for preparing the carbon sink algae liquid based on photosynthetic green algae is to spray the carbon sink algae liquid evenly on the leaf surface of the hawthorn tree, and the carbon sink
  • the present invention has the following advantages:
  • the equipment occupies a small area, simple structure and low cost
  • the carbon sequestration products after filling can be applied to the space outside the forest, so as to generate greater carbon sequestration intensity
  • the carbon dioxide captured by the carbon sink algae liquid becomes the nutrients needed for the life activities of photosynthetic green algae through photosynthesis, and the high concentration of photosynthetic green algae in the carbon sink algae liquid can be applied to the leaves of various trees, making trees The photosynthesis of leaves is improved, thereby increasing the carbon sink of the entire forest.
  • Fig. 1 is a schematic block diagram of the carbon sink algae liquid production equipment based on photosynthetic green algae in the present invention.
  • a kind of carbon sequestration algae liquid production equipment based on photosynthetic green algae provided in an embodiment of the present invention, comprises equipment cavity, and the algae carbon capture tank that is located in the equipment cavity;
  • the algae carbon capture tank is connected to the air treatment equipment through the air inlet pipe, connected to the water treatment equipment through the water inlet pipe, and connected to the high-concentration algae liquid storage tank through the algae liquid outlet pipe;
  • the algae carbon capture tank is provided with an algae concentration monitor, a temperature monitor and an algae liquid inlet pipe, and the algae liquid inlet pipe is used to add photosynthetic green algae liquid;
  • the top of the equipment cavity is provided with lighting equipment, and the high-concentration algae liquid storage tank is connected with the filling equipment.
  • the volume of the algae carbon capture tank is not less than 1 m 3 , which is convenient for operation, storage and transportation.
  • a kind of preparation method of the carbon sequestration algae liquid based on photosynthetic green algae comprises the following steps:
  • the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200ml/min, and air pressure at 0.6Mpa;
  • the water treatment equipment purifies the water, the pH value of the water is controlled at 7.5, and the TDS value is 20, and the purified water is added to the algae carbon capture tank through the water inlet pipe;
  • Pinellia lectin was purified to promote cell division of photosynthetic green algae, and the Pinellia lectin gene was cloned into a high-expression plasmid with a His tag.
  • Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then cultured overnight at 24°C. The next day, the bacterial culture was centrifuged at high speed, and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl, and protease inhibitor cocktail.
  • Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole.
  • the protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge.
  • proteins will be eluted from the column using a 100mM to 1M NaCl gradient.
  • the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size.
  • high-purity pinellia lectin protein can be obtained. Mix the Pinellia lectin protein into the water purified by the water treatment equipment, and add the algae carbon capture tank through the algae liquid inlet pipe;
  • the lighting equipment keeps the light intensity at 2800lux
  • the temperature monitor keeps the temperature at 28°C
  • the algae concentration detector detects the cell concentration of photosynthetic green algae every day;
  • the maximum fixed carbon dioxide rate of photosynthetic green algae is 0.9-2g/(L.d).
  • the present invention is to manufacture equipment with larger carbon sinks similar to forest carbon sinks in a narrower space.
  • Wide application can increase my country's "plain forests", and the carbon dioxide captured at the same time will increase Through photosynthesis, it becomes the nutrients needed for the life activities of algae, and the high-concentration photosynthetic green algae produced by the carbon sink can be used in the forest to increase the photosynthesis of the leaves of the forest, thereby increasing the carbon sink of the forest.
  • the overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with
  • Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge.
  • the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient.
  • the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size.
  • high-purity pinellia lectin protein can be obtained.
  • the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day;
  • the algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment, and the filling operation is carried out to form a carbon sink product.
  • the overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with
  • Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge.
  • the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient.
  • the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size.
  • high-purity pinellia lectin protein can be obtained.
  • the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day;
  • the algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment, and the filling operation is carried out to form a carbon sink product.
  • the overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with
  • Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge.
  • the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient.
  • the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size.
  • high-purity pinellia lectin protein can be obtained.
  • the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day; The algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment for filling operation to form a carbon sink product.
  • the basic overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies Water, the pH value of the water is controlled at 7.5, and the TDS value is 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; Acid, 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/LCuSO 4 5H 2 O, 20mg/L EDTA-Fe are mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the pinellia lectin gene is cloned into a high-expression plasmi
  • Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then cultured overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge.
  • the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient.
  • the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size.
  • high-purity pinellia lectin protein can be obtained.
  • the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day; The algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment for filling operation to form a carbon sink product.
  • the overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with
  • Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge.
  • the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient.
  • the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size.
  • high-purity Pinellia lectin protein can be obtained.
  • the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day;
  • the algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment, and the filling operation is carried out to form a carbon sink product.
  • Embodiment 6 is a diagrammatic representation of Embodiment 6
  • the overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with
  • Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge.
  • the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient.
  • the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size.
  • high-purity pinellia lectin protein can be obtained.
  • the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day;
  • the algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment, and the filling operation is carried out to form a carbon sink product.
  • Embodiment 7 is a diagrammatic representation of Embodiment 7:
  • the overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with
  • Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge.
  • the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient.
  • the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size.
  • high-purity pinellia lectin protein can be obtained. Mix the pinellia lectin protein into the water purified by the water treatment equipment, and pass through the algal liquid inlet pipe
  • the algae concentration detector detects the concentration of photosynthetic green algae cells every day; the whole process lasts for 80 days, and the algae liquid is discharged through the algae liquid outlet pipe into the high-concentration algae liquid storage tank; the algae liquid in the high-concentration algae liquid storage tank is discharged into the solution tank of the filling equipment for filling operation to form a carbon sink product.
  • Embodiment 8 is a diagrammatic representation of Embodiment 8
  • the overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with
  • Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge.
  • the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient.
  • the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size.
  • high-purity pinellia lectin protein can be obtained.
  • the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day;
  • the algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment, and the filling operation is carried out to form a carbon sink product.
  • Embodiment 9 is a diagrammatic representation of Embodiment 9:
  • the overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with
  • Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge.
  • the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient.
  • the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size.
  • high-purity pinellia lectin protein can be obtained.
  • the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day;
  • the algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment, and the filling operation is carried out to form a carbon sink product.
  • the carbon sink strength of algae increases with the increase of culture time. After reaching the peak, continuing to cultivate algae will reduce the carbon sink strength. The best time to remove algae liquid and repeat the culture step is 90 days.
  • the carbon sequestration product high-concentration photosynthetic green algae obtained by embodiment 1-embodiment 9 is respectively applied to 1 mu of Quercus liaoturgisis under the same management conditions, evenly sprayed on the leaves, and 1 liter is applied to each mu of land, and the annual carbon Mobvista, the following data can be obtained:
  • the high-concentration photosynthetic green algae of the carbon sink product obtained through Examples 1-9 are applied to Hawthorn.
  • Select 2 identical areas under the same management conditions, each area is 1 mu, and one of the areas is fertilized normally (comparative example 1), and the other area is fertilized according to the conventional amount, and the leaves are sprayed with carbon sink products with high concentration of photosynthetic green algae 1L, after the hawthorn matured, the sugar content and unsaturated fatty acid content in the hawthorn in the two regions were measured respectively, and the average increase relative to Comparative Example 1 was calculated.
  • the calculation results are shown in the following table:

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Abstract

Disclosed are a photosynthetic green algae-based production apparatus for carbon sink algae liquid, a preparation method, and use. The preparation method comprises the following steps: feeding an algae carbon capture tank with purified air and purified water; adding photosynthetic green algae liquid to the algae carbon capture tank, mixing citric acid, CaCl 2, MgSO 4·7H2O, KH 2PO 4, CuSO 4·5H2O, EDTA-Fe, and purified water, and feeding the algae carbon capture tank with the mixture; mixing a pinellia ternate agglutinin protein with purified water, and feeding the algae carbon capture tank with the mixture; setting a preset illumination intensity by means of an illumination apparatus and keeping the preset illumination intensity, and setting a preset temperature by means of a temperature monitor and keeping the preset temperature; performing continuous culture, monitoring a cell concentration of photosynthetic green algae every day by means of an algae concentration monitor, and when the cell concentration reaches a preset peak value, discharging the carbon sink algae liquid in the algae carbon capture tank into a high-concentration algae liquid storage tank; and discharing the carbon sink algae liquid in the high-concentration algae liquid storage tank into a filling apparatus for filling to form a carbon sink product so as to be suitable for the space outside the forest, so that larger carbon sink intensity can be generated.

Description

基于光合绿藻的碳汇藻液生产设备、制备方法及应用Production equipment, preparation method and application of carbon sequestration algae liquid based on photosynthetic green algae
本申请要求于2022年2月21日提交中国专利局、申请号为202210158236.2、发明名称为“基于光合绿藻的碳汇藻液生产设备、制备方法及应用”的中国专利申请的优先权,其全部内容通过引用结合在本申请中。This application claims the priority of the Chinese patent application submitted to the China Patent Office on February 21, 2022, with the application number 202210158236.2, and the title of the invention is "Carbon sink algae liquid production equipment, preparation method and application based on photosynthetic green algae". The entire contents are incorporated by reference in this application.
技术领域technical field
本发明涉及碳汇藻液生产技术领域,特别涉及一种基于光合绿藻的碳汇藻液生产设备、制备方法及应用。The invention relates to the technical field of carbon sequestration algae liquid production, in particular to a carbon sink algae liquid production equipment, preparation method and application based on photosynthetic green algae.
背景技术Background technique
气候变化是人类共同面临的重大危机和严峻挑战,已经成为国际政治、外交、经济和生态领域的共同关切。应对气候变化应当减缓和适应并重,减缓气候变化是长期的艰巨任务,适应气候变化是更为现实的紧迫任务。林业是受气候变化影响最严重的领域之一,也是我国确定的适应气候变化的重点领域之一。做好林业适应气候变化工作对增强国家整体适应能力,维护生态安全、气候安全具有重大意义。Climate change is a major crisis and severe challenge faced by all mankind, and has become a common concern in the fields of international politics, diplomacy, economy and ecology. To deal with climate change, we should pay equal attention to both mitigation and adaptation. Climate change mitigation is a long-term and arduous task, while adaptation to climate change is a more realistic and urgent task. Forestry is one of the areas most affected by climate change, and it is also one of the key areas for adapting to climate change identified by my country. Doing a good job in forestry adaptation to climate change is of great significance to enhancing the overall adaptability of the country and maintaining ecological security and climate security.
但是我国林业资源禀赋不足,我国森林覆盖率远低于全球31%的平均水平,人均森林面积仅为世界人均的1/4,人均森林蓄积只有世界人均的1/7;湿地率低于全球8.6%的平均水平,人均湿地面积仅为世界人均的1/5,湿地保护压力大、恢复难度大;雾霾天频现,沙尘暴多发,防沙治沙任务重;景观破碎化、物种濒危化加剧,生物多样性保护十分迫切。生态脆弱仍是我国的基本国情,生态产品短缺仍是突出短板,森林、湿地和荒漠生态系统对气候变化比较敏感,气候风险较大。同时,林业适应气候变化工作基础薄弱。林业领域适应气候变化的意识普遍不高、能力相对薄弱、工作体系不够健全、人才队伍比较紧缺,各项工作亟待加强。However, my country's forest resource endowment is insufficient. my country's forest coverage rate is far lower than the global average of 31%. The per capita forest area is only 1/4 of the world's average, and the per capita forest stock is only 1/7 of the world's average. The wetland rate is lower than the global average of 8.6% % of the average level, the per capita wetland area is only 1/5 of the world's per capita, the pressure of wetland protection is great, and the restoration is difficult; the haze is frequent, sandstorms occur frequently, and the task of sand prevention and control is heavy; landscape fragmentation and endangered species are intensified , Biodiversity protection is very urgent. Ecological fragility is still the basic national condition of our country, and the shortage of ecological products is still a prominent shortcoming. Forests, wetlands and desert ecosystems are relatively sensitive to climate change, and climate risks are relatively high. At the same time, the foundation for forestry adaptation to climate change is weak. The awareness of adapting to climate change in the forestry field is generally low, the capacity is relatively weak, the work system is not perfect, and the talent team is in short supply. All work needs to be strengthened urgently.
森林是陆地生态系统中最大的碳库,扩大森林覆盖面积是未来30~50年经济可行、成本较低的减缓和应对气候变化的重要措施。森林具有巨大的汇集二氧化碳的功能,这个功能被称为“碳汇”。同时,毁林以及林地退化、森林火灾和病虫害等,又将其储存的二氧化碳释放到大气中,成为“碳源”。采取措施加强森林生态系统的碳储存和碳汇功能,减少来自森 林的碳排放,已经成为应对气候变化的全球共识和行动,也成为中国两次承诺自主减排的目标之一。但是,现有碳汇产品,一般只用在森林中,且产生的碳汇强度不高。Forests are the largest carbon pool in terrestrial ecosystems, and expanding forest coverage is an important measure to mitigate and respond to climate change that is economically feasible and low-cost in the next 30 to 50 years. Forests have a huge function of sequestering carbon dioxide, which is called "carbon sink". At the same time, deforestation, forest land degradation, forest fires, pests and diseases, etc., release the stored carbon dioxide into the atmosphere and become a "carbon source". Taking measures to strengthen the carbon storage and sink functions of forest ecosystems and reduce carbon emissions from forests has become a global consensus and action to deal with climate change, and it has also become one of the goals of China's two commitments to voluntarily reduce emissions. However, the existing carbon sink products are generally only used in forests, and the carbon sink intensity produced is not high.
发明内容Contents of the invention
基于此,本发明的目的是提供一种基于光合绿藻的碳汇藻液生产设备、制备方法及应用,以提高碳汇强度。Based on this, the object of the present invention is to provide a carbon sink algae liquid production equipment, preparation method and application based on photosynthetic green algae, so as to improve the carbon sink intensity.
第一方面,本发明提供了一种基于光合绿藻的碳汇藻液生产设备,包括设备腔体,以及设于所述设备腔体中的藻类碳捕捉罐;In a first aspect, the present invention provides a carbon sequestration algae liquid production equipment based on photosynthetic green algae, including a device cavity, and an algae carbon capture tank disposed in the device cavity;
所述藻类碳捕捉罐通过进气管连接空气处理设备,通过进水管连接水处理设备,通过出藻液管连接高浓度藻液储存罐;The algae carbon capture tank is connected to the air treatment equipment through the air inlet pipe, connected to the water treatment equipment through the water inlet pipe, and connected to the high-concentration algae liquid storage tank through the algae liquid outlet pipe;
所述藻类碳捕捉罐上设有藻浓度监测仪、温度监测仪和进藻液管,所述进藻液管用于加入光合绿藻液;The algae carbon capture tank is provided with an algae concentration monitor, a temperature monitor and an algae liquid inlet pipe, and the algae liquid inlet pipe is used to add photosynthetic green algae liquid;
所述设备腔体的顶部设有光照设备,所述高浓度藻液储存罐与灌装设备连接。The top of the equipment cavity is provided with lighting equipment, and the high-concentration algae liquid storage tank is connected with the filling equipment.
进一步地,所述藻类碳捕捉罐的体积不小于1m 3Further, the volume of the algae carbon capture tank is not less than 1m 3 .
第一方面,本发明提供了一种基于光合绿藻的碳汇藻液的制备方法,包括以下步骤:In a first aspect, the present invention provides a method for preparing carbon sequestration algae liquid based on photosynthetic green algae, comprising the following steps:
步骤S10,将经空气处理设备处理后的净化空气送入藻类碳捕捉罐中,以及经水处理设备处理后的净化水送入藻类碳捕捉罐;Step S10, sending the purified air treated by the air treatment equipment into the algae carbon capture tank, and the purified water treated by the water treatment equipment into the algae carbon capture tank;
步骤S11,向藻类碳捕捉罐中加入光合绿藻液后,将柠檬酸、CaCl 2、MgSO 4·7H 2O、KH 2PO 4、CuSO 4·5H 2O、EDTA-Fe和净化水混合后,送入藻类碳捕捉罐中; Step S11, after adding photosynthetic green algae liquid into the algae carbon capture tank, mixing citric acid, CaCl 2 , MgSO 4 7H 2 O, KH 2 PO 4 , CuSO 4 5H 2 O, EDTA-Fe and purified water , into the algae carbon capture tank;
步骤S12,将经过多步纯化后的半夏凝集素蛋白质,与净化水混合后,送入藻类碳捕捉罐中;Step S12, mixing the pinellia lectin protein after multi-step purification with purified water, and sending it into the algae carbon capture tank;
步骤S13,通过光照设备设定预设光照强度并保持,温度监测仪设定预设温度并保持;Step S13, setting and maintaining the preset light intensity through the lighting equipment, and setting and maintaining the preset temperature by the temperature monitor;
步骤S14,进行持续培养,并通过藻浓度监测仪每天坚持光合绿藻的细胞浓度,当细胞浓度达到预设峰值时,将藻类碳捕捉罐中的碳汇藻液排入高浓度藻液储存罐中;Step S14, carry out continuous cultivation, and maintain the cell concentration of photosynthetic green algae every day through the algae concentration monitor. When the cell concentration reaches the preset peak value, discharge the carbon sequestration algae liquid in the algae carbon capture tank into the high concentration algae liquid storage tank middle;
步骤S15,将高浓度藻液储存罐中的碳汇藻液排入灌装设备中,进行 灌装,以形成碳汇产品。Step S15, discharge the carbon sequestration algae liquid in the high-concentration algae liquid storage tank into the filling equipment for filling to form carbon sequestration products.
进一步地,所述步骤S12具体包括:Further, the step S12 specifically includes:
步骤S121,将克隆半夏凝集素基因克隆到带有His标签的高表达质粒中,并转化形成细菌培养物进行初步培养后,再用乳糖类似物IPTG诱导以进行再次培养;Step S121, cloning the cloned pinellia lectin gene into a high-expression plasmid with a His tag, and transforming it into a bacterial culture for preliminary culture, and then inducing it with lactose analogue IPTG for secondary culture;
步骤S122,将再次培养的细菌培养物进行高速离心形成细胞沉淀后,采用Tris、NaCl和蛋白酶抑制剂混合物的裂解缓冲液对细胞沉淀进行裂解以形成细胞裂解液;Step S122, after high-speed centrifugation of the recultivated bacterial culture to form a cell pellet, the cell pellet is lysed with a lysis buffer of a mixture of Tris, NaCl and protease inhibitors to form a cell lysate;
步骤S123,细胞裂解液依序经过镍亲和层析、离子交换层析柱和凝胶过滤柱纯化后以得到预设纯度的半夏凝集素蛋白质。In step S123, the cell lysate is sequentially purified by nickel affinity chromatography, ion exchange chromatography column and gel filtration column to obtain Pinellia lectin protein with a preset purity.
进一步地,所述步骤S123具体包括:Further, the step S123 specifically includes:
在细胞裂解液使用镍亲和层析纯化后,将蛋白质用500mM的咪唑洗脱形成初步洗脱液;After the cell lysate was purified by nickel affinity chromatography, the protein was eluted with 500 mM imidazole to form a preliminary eluate;
将初步洗脱液中的蛋白峰收集液注入离子交换层析柱中,基于表面离子电荷使用不同浓度的NaCl进行梯度纯化形成再次洗脱液;Inject the protein peak collection solution in the primary eluent into the ion exchange chromatography column, and use different concentrations of NaCl for gradient purification based on the surface ionic charge to form a second eluent;
将再次洗脱液注入凝胶过滤柱中进行分离纯化以得到预设纯度的半夏凝集素蛋白质。Inject the eluent again into a gel filtration column for separation and purification to obtain Pinellia lectin protein with preset purity.
进一步地,在所述步骤S11中,柠檬酸的浓度为20mg/L,CaCl 2的浓度为2g/L,MgSO 4·7H 2O的浓度为2g/L,KH 2PO 4的浓度为2g/L,CuSO 4·5H 2O的浓度为2mg/L,EDTA-Fe的浓度为20mg/L。 Further, in the step S11, the concentration of citric acid is 20 mg/L, the concentration of CaCl 2 is 2 g/L, the concentration of MgSO 4 ·7H 2 O is 2 g/L, and the concentration of KH 2 PO 4 is 2 g/L. L, the concentration of CuSO 4 ·5H 2 O is 2 mg/L, and the concentration of EDTA-Fe is 20 mg/L.
进一步地,在所述步骤S13中,光照强度为2800lux,温度为28℃。Further, in the step S13, the light intensity is 2800 lux, and the temperature is 28°C.
进一步地,在所述步骤S14中,预设峰值为2000万/毫升,在达到预设峰值前,碳汇藻液的碳汇强度随着培养时间的增加而增强,达到预设峰值后,继续培养会降低碳汇藻液的碳汇强度,且最佳排出碳汇藻液并重复培养步骤的时间为90天。Further, in the step S14, the preset peak value is 20 million/ml. Before reaching the preset peak value, the carbon sink strength of the carbon sequestration algae liquid increases with the increase of culture time. After reaching the preset peak value, continue to Cultivation will reduce the carbon sink intensity of the carbon sink algae liquid, and the best time to discharge the carbon sink algae liquid and repeat the culture step is 90 days.
第三方面,本发明中,上述的基于光合绿藻的碳汇藻液的制备方法制得的碳汇藻液的应用,将该碳汇藻液均匀喷洒在辽东栎的叶面上,该碳汇藻液的浓度越高,辽东栎的光合作用越强、碳汇量增加。In the third aspect, in the present invention, the application of the carbon sink algae liquid prepared by the above-mentioned carbon sink algae liquid based on photosynthetic green algae preparation method, the carbon sink algae liquid is evenly sprayed on the leaf surface of Quercus liaotungensis, and the carbon sink The higher the concentration of algae sink liquid, the stronger the photosynthesis of Quercus liaotungensis and the increase of carbon sink.
第四方面,本发明中,上述的基于光合绿藻的碳汇藻液的制备方法制得的碳汇藻液的应用,将该碳汇藻液均匀喷洒在山楂树的叶面上,该碳汇 藻液的浓度越高,山楂树的光合作用越强、碳汇量增加,成熟山楂的糖度提高、不饱和脂肪酸的含量增加。In the fourth aspect, in the present invention, the application of the carbon sink algae liquid prepared by the above-mentioned method for preparing the carbon sink algae liquid based on photosynthetic green algae is to spray the carbon sink algae liquid evenly on the leaf surface of the hawthorn tree, and the carbon sink The higher the concentration of algae sink, the stronger the photosynthesis of hawthorn, the increase of carbon sink, the sugar content of mature hawthorn and the content of unsaturated fatty acid increased.
相较现有技术,本发明具备以下优点:Compared with the prior art, the present invention has the following advantages:
第一,设备占地面积小,结构简单,成本低;First, the equipment occupies a small area, simple structure and low cost;
第二,灌装后的碳汇产品可适用于森林之外的空间,从而可以产生更大的碳汇强度;Second, the carbon sequestration products after filling can be applied to the space outside the forest, so as to generate greater carbon sequestration intensity;
第三,碳汇藻液捕捉的二氧化碳通过光合作用变成光合绿藻生命活动所需的营养,碳汇藻液中的高浓度光合绿藻又可以应用于各种树木的叶面上,使树木叶面的光合作用提升,从而提升整个森林的碳汇量。Third, the carbon dioxide captured by the carbon sink algae liquid becomes the nutrients needed for the life activities of photosynthetic green algae through photosynthesis, and the high concentration of photosynthetic green algae in the carbon sink algae liquid can be applied to the leaves of various trees, making trees The photosynthesis of leaves is improved, thereby increasing the carbon sink of the entire forest.
说明书附图Instructions attached
图1为本发明中基于光合绿藻的碳汇藻液生产设备的方框示意图。Fig. 1 is a schematic block diagram of the carbon sink algae liquid production equipment based on photosynthetic green algae in the present invention.
如下具体实施方式将结合上述附图进一步说明本发明。The following specific embodiments will further illustrate the present invention in conjunction with the above-mentioned drawings.
具体实施方式Detailed ways
为了便于理解本发明,下面将参照相关附图对本发明进行更全面的描述。附图中给出了本发明的若干实施例。但是,本发明可以以许多不同的形式来实现,并不限于本文所描述的实施例。相反地,提供这些实施例的目的是使对本发明的公开内容更加透彻全面。In order to facilitate the understanding of the present invention, the present invention will be described more fully below with reference to the associated drawings. Several embodiments of the invention are shown in the drawings. However, the present invention can be embodied in many different forms and is not limited to the embodiments described herein. Rather, these embodiments are provided so that the disclosure of the present invention will be thorough and complete.
除非另有定义,本文所使用的所有的技术和科学术语与属于本发明的技术领域的技术人员通常理解的含义相同。本文中在本发明的说明书中所使用的术语只是为了描述具体的实施例的目的,不是旨在于限制本发明。本文所使用的术语“及/或”包括一个或多个相关的所列项目的任意的和所有的组合。Unless otherwise defined, all technical and scientific terms used herein have the same meaning as commonly understood by one of ordinary skill in the technical field of the invention. The terms used herein in the description of the present invention are for the purpose of describing specific embodiments only, and are not intended to limit the present invention. As used herein, the term "and/or" includes any and all combinations of one or more of the associated listed items.
请参阅图1,本发明一实施例中提供的一种基于光合绿藻的碳汇藻液生产设备,包括设备腔体,以及设于所述设备腔体中的藻类碳捕捉罐;Please refer to Fig. 1, a kind of carbon sequestration algae liquid production equipment based on photosynthetic green algae provided in an embodiment of the present invention, comprises equipment cavity, and the algae carbon capture tank that is located in the equipment cavity;
所述藻类碳捕捉罐通过进气管连接空气处理设备,通过进水管连接水处理设备,通过出藻液管连接高浓度藻液储存罐;The algae carbon capture tank is connected to the air treatment equipment through the air inlet pipe, connected to the water treatment equipment through the water inlet pipe, and connected to the high-concentration algae liquid storage tank through the algae liquid outlet pipe;
所述藻类碳捕捉罐上设有藻浓度监测仪、温度监测仪和进藻液管,所述进藻液管用于加入光合绿藻液;The algae carbon capture tank is provided with an algae concentration monitor, a temperature monitor and an algae liquid inlet pipe, and the algae liquid inlet pipe is used to add photosynthetic green algae liquid;
所述设备腔体的顶部设有光照设备,所述高浓度藻液储存罐与灌装设备连接。The top of the equipment cavity is provided with lighting equipment, and the high-concentration algae liquid storage tank is connected with the filling equipment.
需要说明的是,本发明中,所述藻类碳捕捉罐的体积不小于1m 3,便于操作,存放和运输。 It should be noted that, in the present invention, the volume of the algae carbon capture tank is not less than 1 m 3 , which is convenient for operation, storage and transportation.
本发明中,一种基于光合绿藻的碳汇藻液的制备方法,包括以下步骤:Among the present invention, a kind of preparation method of the carbon sequestration algae liquid based on photosynthetic green algae, comprises the following steps:
(1),空气处理设备净化从设备间外吸入的空气,同时保持吸入二氧化碳浓度为33%,氮气50%,通气速率为200ml/min,空气的压强为0.6Mpa;(1), the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200ml/min, and air pressure at 0.6Mpa;
(2),水处理设备净化水,水PH值控制在7.5,TDS值在20,将净化后的水通过进水管加入藻类碳捕捉罐;(2), the water treatment equipment purifies the water, the pH value of the water is controlled at 7.5, and the TDS value is 20, and the purified water is added to the algae carbon capture tank through the water inlet pipe;
(3),将10L光合绿藻液通过进藻液管加入藻类碳捕捉罐;(3), 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe;
(4),将20mg/L柠檬酸、2g/L CaCl 2、2g/L MgSO 4·7H 2O、2g/L KH 2PO 4、2mg/LCuSO 4·5H 2O、20mg/LEDTA-Fe混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐中,以作为光合绿藻生长需要的营养,各个分量均为5g; (4), mix 20mg/L citric acid, 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/LCuSO 4 5H 2 O, 20mg/LEDTA-Fe The water purified by the water treatment equipment is added to the algae carbon capture tank through the algae liquid pipe to serve as the nutrients needed for the growth of photosynthetic green algae, each component is 5g;
(5),半夏凝集素纯化,以促进光合绿藻的细胞分裂,将半夏凝集素基因克隆到带有His标签的高表达质粒中。将转化了带有目的基因的质粒的细菌培养物在37℃培养至OD0.4,用0.2mM乳糖类似物IPTG诱导,然后在24℃培养过夜。第二天,将细菌培养物高速离心,细胞沉淀用含有20mM Tris-pH 7.5、150mM NaCl和蛋白酶抑制剂混合物的裂解缓冲液裂解。细胞裂解液将首先使用镍亲和层析纯化,蛋白质将用500mM咪唑洗脱。然后将蛋白峰收集液注入离子交换层析柱,基于表面离子电荷进一步纯化蛋白质。在此步骤中,蛋白质将使用100mM至1M NaCl梯度从柱中洗脱。最后,来自离子交换柱的洗脱液将被注入凝胶过滤柱,凝胶过滤柱将根据分子大小进一步分离纯化蛋白质。最终,通过这种三步纯化方案可获得高纯度的半夏凝集素蛋白质,将半夏凝集素蛋白质混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;(5) Pinellia lectin was purified to promote cell division of photosynthetic green algae, and the Pinellia lectin gene was cloned into a high-expression plasmid with a His tag. Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then cultured overnight at 24°C. The next day, the bacterial culture was centrifuged at high speed, and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl, and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge. During this step, proteins will be eluted from the column using a 100mM to 1M NaCl gradient. Finally, the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size. Finally, through this three-step purification scheme, high-purity pinellia lectin protein can be obtained. Mix the Pinellia lectin protein into the water purified by the water treatment equipment, and add the algae carbon capture tank through the algae liquid inlet pipe;
(6),光照设备保持光照强度为2800lux;(6), the lighting equipment keeps the light intensity at 2800lux;
(7),温度监测仪保持温度为28℃;(7), the temperature monitor keeps the temperature at 28°C;
(8),藻浓度检测仪每天检测光合绿藻细胞浓度;(8), the algae concentration detector detects the cell concentration of photosynthetic green algae every day;
(9),整个程持续20-100天,将藻液通过出藻液管排入高浓度藻液储存罐;(9), the whole process lasts for 20-100 days, and the algae liquid is discharged into the high-concentration algae liquid storage tank through the algae liquid outlet pipe;
(10),将高浓度藻液储存罐中藻液排入灌装设备溶液罐,进行灌装操作,形成碳汇产品;(10), discharging the algae liquid in the high-concentration algae liquid storage tank into the solution tank of the filling equipment, and performing the filling operation to form a carbon sink product;
(11),重复步骤(1)至步骤(10);(11), repeat step (1) to step (10);
(12),测算步骤(1)至步骤(11),光合绿藻最大固定二氧化碳速率为0.9-2g/(L.d)。(12), measure step (1) to step (11), the maximum fixed carbon dioxide rate of photosynthetic green algae is 0.9-2g/(L.d).
进一步需要明确的是,本发明是在更加狭小的空间,制造出类似森林碳汇一样更大碳汇量的设备,广泛的应用可以使我国增加一一个“平原森林”,同时捕捉的二氧化碳会通过光合作用变成藻类生命活动所需的营养,碳汇产物高浓度光合绿藻又可以用于森林中,使森林的叶面光合作用提升,从而提升森林碳汇量。What needs to be further clarified is that the present invention is to manufacture equipment with larger carbon sinks similar to forest carbon sinks in a narrower space. Wide application can increase my country's "plain forests", and the carbon dioxide captured at the same time will increase Through photosynthesis, it becomes the nutrients needed for the life activities of algae, and the high-concentration photosynthetic green algae produced by the carbon sink can be used in the forest to increase the photosynthesis of the leaves of the forest, thereby increasing the carbon sink of the forest.
下面以具体的实施例来对发明进行详细说明。The invention will be described in detail below with specific embodiments.
实施例1:Example 1:
整体流程步骤为:空气处理设备净化从设备间外吸入的空气,同时保持吸入二氧化碳浓度为33%,氮气为50%,通气速率为200mL/min,空气的压强为0.6Mpa;水处理设备净化水,水PH值控制在7.5,TDS值在20;将净化后的水通过进水管加入藻类碳捕捉罐;将10L光合绿藻液通过进藻液管加入藻类碳捕捉罐;将20mg/L柠檬酸、2g/L CaCl 2、2g/L MgSO 4·7H 2O、2g/L KH 2PO 4、2mg/L CuSO 4·5H 2O、20mg/L EDTA-Fe混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;半夏凝集素纯化,将半夏凝集素基因克隆到带有His标签的高表达质粒中。将转化了带有目的基因的质粒的细菌培养物在37℃培养至OD 0.4,用0.2mM乳糖类似物IPTG诱导,然后在24℃培养过夜。第二天,将细菌培养物高速离心,细胞沉淀用含有20mM Tris-pH 7.5、150mM NaCl和蛋白酶抑制剂混合物的裂解缓冲液裂解。细胞裂解液将首先使用镍亲和层析纯化,蛋白质将用500mM咪唑洗脱。然后将蛋白峰收集液注入离子交换层析柱,基于表面离子电荷进一步纯化蛋白质。在此步骤中,蛋白质将使用100mM至1M NaCl梯度从柱中洗脱。最后,来自离子交换柱的洗脱液将被注入凝胶过滤柱,凝胶过滤柱将根据分子大小进一步分离纯化蛋白质。最终,通过这种三步纯化方案可获得高纯度的半夏凝集素蛋白质,将半夏凝集素蛋白质混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;光照 设备保持光照强度为2800lux;温度控制设备保持温度为28摄氏度;藻浓度检测仪每天检测光合绿藻细胞浓度;整个程持续20天,将藻液通过出藻液管排入高浓度藻液储存罐;将高浓度藻液储存罐中藻液排入灌装设备溶液罐,进行灌装操作,形成碳汇产品。 The overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with a His tag. Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge. In this step, the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient. Finally, the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size. Finally, through this three-step purification scheme, high-purity pinellia lectin protein can be obtained. Mix the pinellia lectin protein into the water purified by the water treatment equipment, and add the algae carbon capture tank through the algae liquid pipe; the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day; The algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment, and the filling operation is carried out to form a carbon sink product.
实施例2:Example 2:
整体流程步骤为:空气处理设备净化从设备间外吸入的空气,同时保持吸入二氧化碳浓度为33%,氮气为50%,通气速率为200mL/min,空气的压强为0.6Mpa;水处理设备净化水,水PH值控制在7.5,TDS值在20;将净化后的水通过进水管加入藻类碳捕捉罐;将10L光合绿藻液通过进藻液管加入藻类碳捕捉罐;将20mg/L柠檬酸、2g/L CaCl 2、2g/L MgSO 4·7H 2O、2g/L KH 2PO 4、2mg/L CuSO 4·5H 2O、20mg/L EDTA-Fe混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;半夏凝集素纯化,将半夏凝集素基因克隆到带有His标签的高表达质粒中。将转化了带有目的基因的质粒的细菌培养物在37℃培养至OD 0.4,用0.2mM乳糖类似物IPTG诱导,然后在24℃培养过夜。第二天,将细菌培养物高速离心,细胞沉淀用含有20mM Tris-pH 7.5、150mM NaCl和蛋白酶抑制剂混合物的裂解缓冲液裂解。细胞裂解液将首先使用镍亲和层析纯化,蛋白质将用500mM咪唑洗脱。然后将蛋白峰收集液注入离子交换层析柱,基于表面离子电荷进一步纯化蛋白质。在此步骤中,蛋白质将使用100mM至1M NaCl梯度从柱中洗脱。最后,来自离子交换柱的洗脱液将被注入凝胶过滤柱,凝胶过滤柱将根据分子大小进一步分离纯化蛋白质。最终,通过这种三步纯化方案可获得高纯度的半夏凝集素蛋白质,将半夏凝集素蛋白质混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;光照设备保持光照强度为2800lux;温度控制设备保持温度为28摄氏度;藻浓度检测仪每天检测光合绿藻细胞浓度;整个程持续30天,将藻液通过出藻液管排入高浓度藻液储存罐;将高浓度藻液储存罐中藻液排入灌装设备溶液罐,进行灌装操作,形成碳汇产品。 The overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with a His tag. Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge. In this step, the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient. Finally, the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size. Finally, through this three-step purification scheme, high-purity pinellia lectin protein can be obtained. Mix the pinellia lectin protein into the water purified by the water treatment equipment, and add the algae carbon capture tank through the algae liquid pipe; the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day; The algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment, and the filling operation is carried out to form a carbon sink product.
实施例3:Example 3:
整体流程步骤为:空气处理设备净化从设备间外吸入的空气,同时保持吸入二氧化碳浓度为33%,氮气为50%,通气速率为200mL/min,空 气的压强为0.6Mpa;水处理设备净化水,水PH值控制在7.5,TDS值在20;将净化后的水通过进水管加入藻类碳捕捉罐;将10L光合绿藻液通过进藻液管加入藻类碳捕捉罐;将20mg/L柠檬酸、2g/L CaCl 2、2g/L MgSO 4·7H 2O、2g/L KH 2PO 4、2mg/L CuSO 4·5H 2O、20mg/L EDTA-Fe混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;半夏凝集素纯化,将半夏凝集素基因克隆到带有His标签的高表达质粒中。将转化了带有目的基因的质粒的细菌培养物在37℃培养至OD 0.4,用0.2mM乳糖类似物IPTG诱导,然后在24℃培养过夜。第二天,将细菌培养物高速离心,细胞沉淀用含有20mM Tris-pH 7.5、150mM NaCl和蛋白酶抑制剂混合物的裂解缓冲液裂解。细胞裂解液将首先使用镍亲和层析纯化,蛋白质将用500mM咪唑洗脱。然后将蛋白峰收集液注入离子交换层析柱,基于表面离子电荷进一步纯化蛋白质。在此步骤中,蛋白质将使用100mM至1M NaCl梯度从柱中洗脱。最后,来自离子交换柱的洗脱液将被注入凝胶过滤柱,凝胶过滤柱将根据分子大小进一步分离纯化蛋白质。最终,通过这种三步纯化方案可获得高纯度的半夏凝集素蛋白质,将半夏凝集素蛋白质混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;光照设备保持光照强度为2800lux;温度控制设备保持温度为28摄氏度;藻浓度检测仪每天检测光合绿藻细胞浓度;整个程持续40天,将藻液通过出藻液管排入高浓度藻液储存罐;将高浓度藻液储存罐中藻液排入灌装设备溶液罐,进行灌装操作,形成碳汇产品。 The overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with a His tag. Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge. In this step, the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient. Finally, the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size. Finally, through this three-step purification scheme, high-purity pinellia lectin protein can be obtained. Mix the pinellia lectin protein into the water purified by the water treatment equipment, and add the algae carbon capture tank through the algae liquid pipe; the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day; The algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment for filling operation to form a carbon sink product.
实施例4:Example 4:
基整体流程步骤为:空气处理设备净化从设备间外吸入的空气,同时保持吸入二氧化碳浓度为33%,氮气为50%,通气速率为200mL/min,空气的压强为0.6Mpa;水处理设备净化水,水PH值控制在7.5,TDS值在20;将净化后的水通过进水管加入藻类碳捕捉罐;将10L光合绿藻液通过进藻液管加入藻类碳捕捉罐;将20mg/L柠檬酸、2g/L CaCl 2、2g/L MgSO 4·7H 2O、2g/L KH 2PO 4、2mg/LCuSO 4·5H 2O、20mg/L EDTA-Fe混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;半夏凝集素纯化,将半夏凝集素基因克隆到带有His标签的高表达质粒中。将转化了带有目的基因的质粒的细菌培养物在37℃培养至OD0.4,用0.2mM乳糖 类似物IPTG诱导,然后在24℃培养过夜。第二天,将细菌培养物高速离心,细胞沉淀用含有20mM Tris-pH 7.5、150mM NaCl和蛋白酶抑制剂混合物的裂解缓冲液裂解。细胞裂解液将首先使用镍亲和层析纯化,蛋白质将用500mM咪唑洗脱。然后将蛋白峰收集液注入离子交换层析柱,基于表面离子电荷进一步纯化蛋白质。在此步骤中,蛋白质将使用100mM至1M NaCl梯度从柱中洗脱。最后,来自离子交换柱的洗脱液将被注入凝胶过滤柱,凝胶过滤柱将根据分子大小进一步分离纯化蛋白质。最终,通过这种三步纯化方案可获得高纯度的半夏凝集素蛋白质,将半夏凝集素蛋白质混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;光照设备保持光照强度为2800lux;温度控制设备保持温度为28摄氏度;藻浓度检测仪每天检测光合绿藻细胞浓度;整个程持续50天,将藻液通过出藻液管排入高浓度藻液储存罐;将高浓度藻液储存罐中藻液排入灌装设备溶液罐,进行灌装操作,形成碳汇产品。 The basic overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies Water, the pH value of the water is controlled at 7.5, and the TDS value is 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; Acid, 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/LCuSO 4 5H 2 O, 20mg/L EDTA-Fe are mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the pinellia lectin gene is cloned into a high-expression plasmid with a His tag. Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then cultured overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge. In this step, the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient. Finally, the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size. Finally, through this three-step purification scheme, high-purity pinellia lectin protein can be obtained. Mix the pinellia lectin protein into the water purified by the water treatment equipment, and add the algae carbon capture tank through the algae liquid pipe; the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day; The algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment for filling operation to form a carbon sink product.
实施例5:Example 5:
整体流程步骤为:空气处理设备净化从设备间外吸入的空气,同时保持吸入二氧化碳浓度为33%,氮气为50%,通气速率为200mL/min,空气的压强为0.6Mpa;水处理设备净化水,水PH值控制在7.5,TDS值在20;将净化后的水通过进水管加入藻类碳捕捉罐;将10L光合绿藻液通过进藻液管加入藻类碳捕捉罐;将20mg/L柠檬酸、2g/L CaCl 2、2g/L MgSO 4·7H 2O、2g/L KH 2PO 4、2mg/L CuSO 4·5H 2O、20mg/L EDTA-Fe混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;半夏凝集素纯化,将半夏凝集素基因克隆到带有His标签的高表达质粒中。将转化了带有目的基因的质粒的细菌培养物在37℃培养至OD 0.4,用0.2mM乳糖类似物IPTG诱导,然后在24℃培养过夜。第二天,将细菌培养物高速离心,细胞沉淀用含有20mM Tris-pH 7.5、150mM NaCl和蛋白酶抑制剂混合物的裂解缓冲液裂解。细胞裂解液将首先使用镍亲和层析纯化,蛋白质将用500mM咪唑洗脱。然后将蛋白峰收集液注入离子交换层析柱,基于表面离子电荷进一步纯化蛋白质。在此步骤中,蛋白质将使用100mM至1M NaCl梯度从柱中洗脱。最后,来自离子交换柱的洗脱液将被注入凝胶过滤柱,凝胶过滤柱将根据分子大小进一步分离纯化蛋白质。最终, 通过这种三步纯化方案可获得高纯度的半夏凝集素蛋白质,将半夏凝集素蛋白质混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;光照设备保持光照强度为2800lux;温度控制设备保持温度为28摄氏度;藻浓度检测仪每天检测光合绿藻细胞浓度;整个程持续60天,将藻液通过出藻液管排入高浓度藻液储存罐;将高浓度藻液储存罐中藻液排入灌装设备溶液罐,进行灌装操作,形成碳汇产品。 The overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with a His tag. Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge. In this step, the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient. Finally, the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size. Finally, through this three-step purification scheme, high-purity Pinellia lectin protein can be obtained. Mix the pinellia lectin protein into the water purified by the water treatment equipment, and add the algae carbon capture tank through the algae liquid pipe; the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day; The algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment, and the filling operation is carried out to form a carbon sink product.
实施例6:Embodiment 6:
整体流程步骤为:空气处理设备净化从设备间外吸入的空气,同时保持吸入二氧化碳浓度为33%,氮气为50%,通气速率为200mL/min,空气的压强为0.6Mpa;水处理设备净化水,水PH值控制在7.5,TDS值在20;将净化后的水通过进水管加入藻类碳捕捉罐;将10L光合绿藻液通过进藻液管加入藻类碳捕捉罐;将20mg/L柠檬酸、2g/L CaCl 2、2g/L MgSO 4·7H 2O、2g/L KH 2PO 4、2mg/L CuSO 4·5H 2O、20mg/L EDTA-Fe混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;半夏凝集素纯化,将半夏凝集素基因克隆到带有His标签的高表达质粒中。将转化了带有目的基因的质粒的细菌培养物在37℃培养至OD 0.4,用0.2mM乳糖类似物IPTG诱导,然后在24℃培养过夜。第二天,将细菌培养物高速离心,细胞沉淀用含有20mM Tris-pH 7.5、150mM NaCl和蛋白酶抑制剂混合物的裂解缓冲液裂解。细胞裂解液将首先使用镍亲和层析纯化,蛋白质将用500mM咪唑洗脱。然后将蛋白峰收集液注入离子交换层析柱,基于表面离子电荷进一步纯化蛋白质。在此步骤中,蛋白质将使用100mM至1M NaCl梯度从柱中洗脱。最后,来自离子交换柱的洗脱液将被注入凝胶过滤柱,凝胶过滤柱将根据分子大小进一步分离纯化蛋白质。最终,通过这种三步纯化方案可获得高纯度的半夏凝集素蛋白质,将半夏凝集素蛋白质混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;光照设备保持光照强度为2800lux;温度控制设备保持温度为28摄氏度;藻浓度检测仪每天检测光合绿藻细胞浓度;整个程持续70天,将藻液通过出藻液管排入高浓度藻液储存罐;将高浓度藻液储存罐中藻液排入灌装设备溶液罐,进行灌装操作,形成碳汇产品。 The overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with a His tag. Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge. In this step, the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient. Finally, the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size. Finally, through this three-step purification scheme, high-purity pinellia lectin protein can be obtained. Mix the pinellia lectin protein into the water purified by the water treatment equipment, and add the algae carbon capture tank through the algae liquid pipe; the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day; The algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment, and the filling operation is carried out to form a carbon sink product.
实施例7:Embodiment 7:
整体流程步骤为:空气处理设备净化从设备间外吸入的空气,同时保持吸入二氧化碳浓度为33%,氮气为50%,通气速率为200mL/min,空气的压强为0.6Mpa;水处理设备净化水,水PH值控制在7.5,TDS值在20;将净化后的水通过进水管加入藻类碳捕捉罐;将10L光合绿藻液通过进藻液管加入藻类碳捕捉罐;将20mg/L柠檬酸、2g/L CaCl 2、2g/L MgSO 4·7H 2O、2g/L KH 2PO 4、2mg/L CuSO 4·5H 2O、20mg/L EDTA-Fe混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;半夏凝集素纯化,将半夏凝集素基因克隆到带有His标签的高表达质粒中。将转化了带有目的基因的质粒的细菌培养物在37℃培养至OD 0.4,用0.2mM乳糖类似物IPTG诱导,然后在24℃培养过夜。第二天,将细菌培养物高速离心,细胞沉淀用含有20mM Tris-pH 7.5、150mM NaCl和蛋白酶抑制剂混合物的裂解缓冲液裂解。细胞裂解液将首先使用镍亲和层析纯化,蛋白质将用500mM咪唑洗脱。然后将蛋白峰收集液注入离子交换层析柱,基于表面离子电荷进一步纯化蛋白质。在此步骤中,蛋白质将使用100mM至1M NaCl梯度从柱中洗脱。最后,来自离子交换柱的洗脱液将被注入凝胶过滤柱,凝胶过滤柱将根据分子大小进一步分离纯化蛋白质。最终,通过这种三步纯化方案可获得高纯度的半夏凝集素蛋白质,将半夏凝集素蛋白质混合入水处理设备净化后的水,通过进藻液管 The overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with a His tag. Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge. In this step, the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient. Finally, the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size. Finally, through this three-step purification scheme, high-purity pinellia lectin protein can be obtained. Mix the pinellia lectin protein into the water purified by the water treatment equipment, and pass through the algal liquid inlet pipe
加入藻类碳捕捉罐;光照设备保持光照强度为2800lux;温度控制设备保持温度为28摄氏度;藻浓度检测仪每天检测光合绿藻细胞浓度;整个程持续80天,将藻液通过出藻液管排入高浓度藻液储存罐;将高浓度藻液储存罐中藻液排入灌装设备溶液罐,进行灌装操作,形成碳汇产品。Add the algae carbon capture tank; the lighting equipment keeps the light intensity at 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day; the whole process lasts for 80 days, and the algae liquid is discharged through the algae liquid outlet pipe into the high-concentration algae liquid storage tank; the algae liquid in the high-concentration algae liquid storage tank is discharged into the solution tank of the filling equipment for filling operation to form a carbon sink product.
实施例8:Embodiment 8:
整体流程步骤为:空气处理设备净化从设备间外吸入的空气,同时保持吸入二氧化碳浓度为33%,氮气为50%,通气速率为200mL/min,空气的压强为0.6Mpa;水处理设备净化水,水PH值控制在7.5,TDS值在20;将净化后的水通过进水管加入藻类碳捕捉罐;将10L光合绿藻液通过进藻液管加入藻类碳捕捉罐;将20mg/L柠檬酸、2g/L CaCl 2、2g/L MgSO 4·7H 2O、2g/L KH 2PO 4、2mg/L CuSO 4·5H 2O、20mg/L EDTA-Fe混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;半夏凝集素 纯化,将半夏凝集素基因克隆到带有His标签的高表达质粒中。将转化了带有目的基因的质粒的细菌培养物在37℃培养至OD 0.4,用0.2mM乳糖类似物IPTG诱导,然后在24℃培养过夜。第二天,将细菌培养物高速离心,细胞沉淀用含有20mM Tris-pH 7.5、150mM NaCl和蛋白酶抑制剂混合物的裂解缓冲液裂解。细胞裂解液将首先使用镍亲和层析纯化,蛋白质将用500mM咪唑洗脱。然后将蛋白峰收集液注入离子交换层析柱,基于表面离子电荷进一步纯化蛋白质。在此步骤中,蛋白质将使用100mM至1M NaCl梯度从柱中洗脱。最后,来自离子交换柱的洗脱液将被注入凝胶过滤柱,凝胶过滤柱将根据分子大小进一步分离纯化蛋白质。最终,通过这种三步纯化方案可获得高纯度的半夏凝集素蛋白质,将半夏凝集素蛋白质混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;光照设备保持光照强度为2800lux;温度控制设备保持温度为28摄氏度;藻浓度检测仪每天检测光合绿藻细胞浓度;整个程持续90天,将藻液通过出藻液管排入高浓度藻液储存罐;将高浓度藻液储存罐中藻液排入灌装设备溶液罐,进行灌装操作,形成碳汇产品。 The overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with a His tag. Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge. In this step, the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient. Finally, the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size. Finally, through this three-step purification scheme, high-purity pinellia lectin protein can be obtained. Mix the pinellia lectin protein into the water purified by the water treatment equipment, and add the algae carbon capture tank through the algae liquid pipe; the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day; The algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment, and the filling operation is carried out to form a carbon sink product.
实施例9:Embodiment 9:
整体流程步骤为:空气处理设备净化从设备间外吸入的空气,同时保持吸入二氧化碳浓度为33%,氮气为50%,通气速率为200mL/min,空气的压强为0.6Mpa;水处理设备净化水,水PH值控制在7.5,TDS值在20;将净化后的水通过进水管加入藻类碳捕捉罐;将10L光合绿藻液通过进藻液管加入藻类碳捕捉罐;将20mg/L柠檬酸、2g/L CaCl 2、2g/L MgSO 4·7H 2O、2g/L KH 2PO 4、2mg/L CuSO 4·5H 2O、20mg/L EDTA-Fe混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;半夏凝集素纯化,将半夏凝集素基因克隆到带有His标签的高表达质粒中。将转化了带有目的基因的质粒的细菌培养物在37℃培养至OD 0.4,用0.2mM乳糖类似物IPTG诱导,然后在24℃培养过夜。第二天,将细菌培养物高速离心,细胞沉淀用含有20mM Tris-pH 7.5、150mM NaCl和蛋白酶抑制剂混合物的裂解缓冲液裂解。细胞裂解液将首先使用镍亲和层析纯化,蛋白质将用500mM咪唑洗脱。然后将蛋白峰收集液注入离子交换层析柱,基于表面离子电荷进一步纯化蛋白质。在此步骤中,蛋白质将使用100mM至 1M NaCl梯度从柱中洗脱。最后,来自离子交换柱的洗脱液将被注入凝胶过滤柱,凝胶过滤柱将根据分子大小进一步分离纯化蛋白质。最终,通过这种三步纯化方案可获得高纯度的半夏凝集素蛋白质,将半夏凝集素蛋白质混合入水处理设备净化后的水,通过进藻液管加入藻类碳捕捉罐;光照设备保持光照强度为2800lux;温度控制设备保持温度为28摄氏度;藻浓度检测仪每天检测光合绿藻细胞浓度;整个程持续100天,将藻液通过出藻液管排入高浓度藻液储存罐;将高浓度藻液储存罐中藻液排入灌装设备溶液罐,进行灌装操作,形成碳汇产品。 The overall process steps are: the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, nitrogen at 50%, ventilation rate at 200mL/min, and air pressure at 0.6Mpa; water treatment equipment purifies water , the water pH value is controlled at 7.5, and the TDS value is at 20; the purified water is added to the algae carbon capture tank through the water inlet pipe; 10L of photosynthetic green algae liquid is added to the algae carbon capture tank through the algae liquid inlet pipe; , 2g/L CaCl 2 , 2g/L MgSO 4 7H 2 O, 2g/L KH 2 PO 4 , 2mg/L CuSO 4 5H 2 O, 20mg/L EDTA-Fe mixed into the purified water of the water treatment equipment, Add the algae carbon capture tank through the algae liquid tube; the pinellia lectin is purified, and the Pinellia lectin gene is cloned into a high-expression plasmid with a His tag. Bacterial cultures transformed with a plasmid carrying the gene of interest were grown at 37°C to OD 0.4, induced with 0.2 mM lactose analogue IPTG, and then grown overnight at 24°C. The next day, the bacterial culture was high-speed centrifuged and the cell pellet was lysed with lysis buffer containing 20 mM Tris-pH 7.5, 150 mM NaCl and protease inhibitor cocktail. Cell lysates will first be purified using nickel affinity chromatography and proteins will be eluted with 500 mM imidazole. The protein peak pool is then injected into an ion-exchange column to further purify the protein based on its surface ionic charge. In this step, the protein will be eluted from the column using a 100 mM to 1 M NaCl gradient. Finally, the eluate from the ion exchange column will be injected into the gel filtration column, which will further separate and purify the protein according to the molecular size. Finally, through this three-step purification scheme, high-purity pinellia lectin protein can be obtained. Mix the pinellia lectin protein into the water purified by the water treatment equipment, and add the algae carbon capture tank through the algae liquid pipe; the lighting equipment keeps the light The intensity is 2800lux; the temperature control equipment keeps the temperature at 28 degrees Celsius; the algae concentration detector detects the concentration of photosynthetic green algae cells every day; The algae liquid in the concentration algae liquid storage tank is discharged into the solution tank of the filling equipment, and the filling operation is carried out to form a carbon sink product.
试验例1:Test example 1:
通过测算实施例1-实施例9的光合绿藻固碳,可得到如下数据:By calculating the carbon fixation of photosynthetic green algae of embodiment 1-embodiment 9, the following data can be obtained:
Figure PCTCN2022131687-appb-000001
Figure PCTCN2022131687-appb-000001
由上表可以看出,由于碳汇藻类细胞本身的繁殖到达峰值浓度为2000万/毫升,在It can be seen from the above table that due to the reproduction of the carbon sink algae cells themselves, the peak concentration is 20 million/ml.
达到峰值前,藻类碳汇强度随着培养时间的增加而增强,到达峰值后,继续培养藻类会降低碳汇强度,最佳排除藻液并重复培养步骤时间为90天。Before reaching the peak, the carbon sink strength of algae increases with the increase of culture time. After reaching the peak, continuing to cultivate algae will reduce the carbon sink strength. The best time to remove algae liquid and repeat the culture step is 90 days.
试验例2:Test example 2:
通过实施例1-实施例9得到的碳汇产品高浓度光合绿藻,分别应用于相同管理条件下的1亩辽东栎,均匀喷洒在叶面,每亩地施用1升,测算一年的碳汇量,可得到如下数据:The carbon sequestration product high-concentration photosynthetic green algae obtained by embodiment 1-embodiment 9 is respectively applied to 1 mu of Quercus liaotungensis under the same management conditions, evenly sprayed on the leaves, and 1 liter is applied to each mu of land, and the annual carbon Mobvista, the following data can be obtained:
Figure PCTCN2022131687-appb-000002
Figure PCTCN2022131687-appb-000002
由上表可以看出,光合绿藻的浓度越高,可以更加增加树木的光合作用,使得树木的碳汇量增加。It can be seen from the above table that the higher the concentration of photosynthetic green algae, the more photosynthesis of trees can be increased, and the carbon sink of trees can be increased.
试验例3Test example 3
通过实施例1-实施例9得到的碳汇产品高浓度光合绿藻,应用于山楂。选取同一管理条件下的2个相同的区域,每个区域1亩,对其中一个 区域采用正常施肥(对比例1),一个区域按常规用量施肥,叶面喷施碳汇产品高浓度光合绿藻1L,山楂成熟后,分别测定2个区域山楂中的含糖量和不饱和脂肪酸含量,计算出相对于对比例1的平均增加量,计算结果如下表所示:The high-concentration photosynthetic green algae of the carbon sink product obtained through Examples 1-9 are applied to Hawthorn. Select 2 identical areas under the same management conditions, each area is 1 mu, and one of the areas is fertilized normally (comparative example 1), and the other area is fertilized according to the conventional amount, and the leaves are sprayed with carbon sink products with high concentration of photosynthetic green algae 1L, after the hawthorn matured, the sugar content and unsaturated fatty acid content in the hawthorn in the two regions were measured respectively, and the average increase relative to Comparative Example 1 was calculated. The calculation results are shown in the following table:
Figure PCTCN2022131687-appb-000003
Figure PCTCN2022131687-appb-000003
由上表可以看出,光合绿藻的浓度越高,越能更加增加山楂的光合作用,使得山楂的糖度提高,同时增加不饱和脂肪酸效果更加明显。It can be seen from the above table that the higher the concentration of photosynthetic green algae, the more the photosynthesis of hawthorn can be increased, the sugar content of hawthorn will be increased, and the effect of increasing unsaturated fatty acids will be more obvious.
本说明书中,各个实施例采用递进的方式描述,每个实施例重点说明的都是与其它实施例的不同之处,各个实施例之间相同或相似部分互相参见即可。且以上所述实施例仅表达了本发明的几种实施方式,其描述较为具体和详细,但并不能因此而理解为对本发明专利范围的限制。应当指出的是,对于本领域的普通技术人员来说,在不脱离本发明构思的前提下,还可以做出若干变形和改进,这些都属于本发明的保护范围。因此,本发明专利的保护范围应以所附权利要求为准。In this specification, various embodiments are described in a progressive manner, each embodiment focuses on the difference from other embodiments, and the same or similar parts of various embodiments can be referred to each other. Moreover, the above-mentioned embodiments only express several implementation modes of the present invention, and the descriptions thereof are relatively specific and detailed, but should not be construed as limiting the patent scope of the present invention. It should be noted that, for those skilled in the art, several modifications and improvements can be made without departing from the concept of the present invention, and these all belong to the protection scope of the present invention. Therefore, the protection scope of the patent for the present invention should be based on the appended claims.
以上所述仅是本发明的优选实施方式,应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明原理的前提下,还可以做出若干改进和润饰,这些改进和润饰也应视为本发明的保护范围。The above is only a preferred embodiment of the present invention, it should be pointed out that, for those of ordinary skill in the art, without departing from the principle of the present invention, some improvements and modifications can also be made, and these improvements and modifications can also be made. It should be regarded as the protection scope of the present invention.

Claims (18)

  1. 一种基于光合绿藻的碳汇藻液生产设备,其特征在于:包括设备腔体,以及设于所述设备腔体中的藻类碳捕捉罐;A carbon sequestration algae liquid production device based on photosynthetic green algae, characterized in that: it includes a device cavity, and an algae carbon capture tank arranged in the device cavity;
    所述藻类碳捕捉罐通过进气管连接空气处理设备,通过进水管连接水处理设备,通过出藻液管连接高浓度藻液储存罐;The algae carbon capture tank is connected to the air treatment equipment through the air inlet pipe, connected to the water treatment equipment through the water inlet pipe, and connected to the high-concentration algae liquid storage tank through the algae liquid outlet pipe;
    所述藻类碳捕捉罐上设有藻浓度监测仪、温度监测仪和进藻液管,所述进藻液管用于加入光合绿藻液;The algae carbon capture tank is provided with an algae concentration monitor, a temperature monitor and an algae liquid inlet pipe, and the algae liquid inlet pipe is used to add photosynthetic green algae liquid;
    所述设备腔体的顶部设有光照设备,所述高浓度藻液储存罐与灌装设备连接。The top of the equipment cavity is provided with lighting equipment, and the high-concentration algae liquid storage tank is connected with the filling equipment.
  2. 根据权利要求1所述的基于光合绿藻的碳汇藻液生产设备,其特征在于,所述藻类碳捕捉罐的体积不小于1m 3The carbon sequestration algae liquid production equipment based on photosynthetic green algae according to claim 1, characterized in that the volume of the algae carbon capture tank is not less than 1 m 3 .
  3. 一种基于光合绿藻的碳汇藻液的制备方法,其特征在于,包括以下步骤:A method for preparing carbon sequestration algae liquid based on photosynthetic green algae, characterized in that it comprises the following steps:
    步骤S10,将经空气处理设备处理后的净化空气送入藻类碳捕捉罐中,以及经水处理设备处理后的净化水送入藻类碳捕捉罐;Step S10, sending the purified air treated by the air treatment equipment into the algae carbon capture tank, and the purified water treated by the water treatment equipment into the algae carbon capture tank;
    步骤S11,向藻类碳捕捉罐中加入光合绿藻液后,将柠檬酸、CaCl 2、MgSO 4·7H 2O、KH 2PO 4、CuSO 4·5H 2O、EDTA-Fe和净化水混合后,送入藻类碳捕捉罐中; Step S11, after adding photosynthetic green algae liquid into the algae carbon capture tank, mixing citric acid, CaCl 2 , MgSO 4 7H 2 O, KH 2 PO 4 , CuSO 4 5H 2 O, EDTA-Fe and purified water , into the algae carbon capture tank;
    步骤S12,将经过多步纯化后的半夏凝集素蛋白质,与净化水混合后,送入藻类碳捕捉罐中;Step S12, mixing the pinellia lectin protein after multi-step purification with purified water, and sending it into the algae carbon capture tank;
    步骤S13,通过光照设备设定预设光照强度并保持,温度监测仪设定预设温度并保持;Step S13, setting and maintaining the preset light intensity through the lighting equipment, and setting and maintaining the preset temperature by the temperature monitor;
    步骤S14,进行持续培养,并通过藻浓度监测仪每天检测光合绿藻的细胞浓度,当细胞浓度达到预设峰值时,将藻类碳捕捉罐中的碳汇藻液排入高浓度藻液储存罐中;Step S14, carry out continuous cultivation, and detect the cell concentration of photosynthetic green algae every day through the algae concentration monitor. When the cell concentration reaches the preset peak value, discharge the carbon sequestration algae liquid in the algae carbon capture tank into the high concentration algae liquid storage tank middle;
    步骤S15,将高浓度藻液储存罐中的碳汇藻液排入灌装设备中,进行灌装,以形成碳汇产品。Step S15, discharging the carbon sequestration algae liquid in the high-concentration algae liquid storage tank into the filling equipment for filling to form a carbon sink product.
  4. 根据权利要求3所述的制备方法,其特征在于,所述步骤S10中,所述空气处理设备净化从设备间外吸入的空气,同时保持吸入二氧化碳浓 度为33%,氮气浓度为50%,通气速率为200mL/min,空气的压强为0.6Mpa。The preparation method according to claim 3, characterized in that, in the step S10, the air treatment equipment purifies the air inhaled from the outside of the equipment room, while maintaining the inhaled carbon dioxide concentration at 33%, the nitrogen concentration at 50%, and ventilation The rate is 200mL/min, and the air pressure is 0.6Mpa.
  5. 根据权利要求3所述的制备方法,其特征在于,所述步骤S10中,所述水处理设备处理后的净化水pH值为7.5,TDS值为20。The preparation method according to claim 3, characterized in that, in the step S10, the purified water treated by the water treatment equipment has a pH value of 7.5 and a TDS value of 20.
  6. 根据权利要求3所述的制备方法,其特征在于,所述步骤S12具体包括:The preparation method according to claim 3, wherein said step S12 specifically comprises:
    步骤S121,将克隆半夏凝集素基因克隆到带有His标签的高表达质粒中,并转化形成细菌培养物进行初步培养后,再用乳糖类似物IPTG诱导以进行再次培养;Step S121, cloning the cloned pinellia lectin gene into a high-expression plasmid with a His tag, and transforming it into a bacterial culture for preliminary culture, and then inducing it with lactose analogue IPTG for secondary culture;
    步骤S122,将再次培养的细菌培养物进行高速离心形成细胞沉淀后,采用Tris、NaCl和蛋白酶抑制剂混合物的裂解缓冲液对细胞沉淀进行裂解以形成细胞裂解液;Step S122, after high-speed centrifugation of the recultivated bacterial culture to form a cell pellet, the cell pellet is lysed with a lysis buffer of a mixture of Tris, NaCl and protease inhibitors to form a cell lysate;
    步骤S123,细胞裂解液依序经过镍亲和层析、离子交换层析柱和凝胶过滤柱纯化后,得到预设纯度的半夏凝集素蛋白质。In step S123, the cell lysate is sequentially purified by nickel affinity chromatography, ion exchange chromatography column and gel filtration column to obtain pinellia lectin protein with preset purity.
  7. 根据权利要求6所述的制备方法,其特征在于,所述步骤S121中,所述初步培养的温度为37℃,进行所述初步培养至OD值为0.4。The preparation method according to claim 6, characterized in that, in the step S121, the temperature of the preliminary cultivation is 37°C, and the preliminary cultivation is carried out until the OD value is 0.4.
  8. 根据权利要求6所述的制备方法,其特征在于,所述步骤S121中,所述乳糖类似物的浓度为0.2mM,所述再次培养为在24℃培养过夜。The preparation method according to claim 6, characterized in that, in the step S121, the concentration of the lactose analogue is 0.2 mM, and the re-cultivation is overnight at 24°C.
  9. 根据权利要求6所述的制备方法,其特征在于,所述步骤S122中,所述裂解缓冲液中Tris的pH值为7.5,浓度为20mM,所述NaCl的浓度为150mM。The preparation method according to claim 6, characterized in that, in the step S122, the pH value of Tris in the lysis buffer is 7.5, the concentration is 20 mM, and the concentration of NaCl is 150 mM.
  10. 根据权利要求6所述的制备方法,其特征在于,所述步骤S123具体包括:The preparation method according to claim 6, wherein the step S123 specifically comprises:
    在细胞裂解液使用镍亲和层析纯化后,将蛋白质用500mM的咪唑洗脱,形成初步洗脱液;After the cell lysate was purified by nickel affinity chromatography, the protein was eluted with 500 mM imidazole to form a preliminary eluate;
    将初步洗脱液中的蛋白峰收集液注入离子交换层析柱中,基于表面离子电荷使用不同浓度的NaCl进行梯度纯化,形成再次洗脱液;Inject the protein peak collection solution in the primary eluent into the ion exchange chromatography column, and use different concentrations of NaCl for gradient purification based on the surface ionic charge to form a second eluent;
    将再次洗脱液注入凝胶过滤柱中,进行分离纯化,得到预设纯度的半夏凝集素蛋白质。Inject the eluate again into the gel filtration column for separation and purification to obtain Pinellia lectin protein with preset purity.
  11. 根据权利要求10所述的制备方法,其特征在于,所述不同浓度的 NaCl的浓度范围为100mM~1M。The preparation method according to claim 10, characterized in that the concentration range of the NaCl of different concentrations is 100mM~1M.
  12. 根据权利要求3所述的制备方法,其特征在于,在所述步骤S11中,柠檬酸的浓度为20mg/L,CaCl 2的浓度为2g/L,MgSO 4·7H 2O的浓度为2g/L,KH 2PO 4的浓度为2g/L,CuSO 4·5H 2O的浓度为2mg/L,EDTA-Fe的浓度为20mg/L。 The preparation method according to claim 3, characterized in that, in the step S11, the concentration of citric acid is 20 mg/L, the concentration of CaCl 2 is 2 g/L, and the concentration of MgSO 4 ·7H 2 O is 2 g/L. L, the concentration of KH 2 PO 4 is 2g/L, the concentration of CuSO 4 ·5H 2 O is 2mg/L, and the concentration of EDTA-Fe is 20mg/L.
  13. 根据权利要求3所述的制备方法,其特征在于,在所述步骤S13中,光照强度为2800lux,温度为28℃。The preparation method according to claim 3, characterized in that, in the step S13, the light intensity is 2800 lux, and the temperature is 28°C.
  14. 根据权利要求3所述的制备方法,其特征在于,在所述步骤S14中,所述持续培养的时间为20~100天。The preparation method according to claim 3, characterized in that, in the step S14, the duration of the continuous culture is 20-100 days.
  15. 根据权利要求3所述的制备方法,其特征在于,在所述步骤S14中,预设峰值为2000万/毫升,在达到所述预设峰值前,碳汇藻液的碳汇强度随着培养时间的增加而增强,达到预设峰值后,继续培养会降低碳汇藻液的碳汇强度,且最佳排出碳汇藻液并重复培养步骤的时间为90天。The preparation method according to claim 3, characterized in that, in the step S14, the preset peak value is 20 million/ml, and before reaching the preset peak value, the carbon sink intensity of the carbon sink algae liquid increases with the cultivation After reaching the preset peak value, continuing to cultivate will reduce the carbon sink strength of the carbon sink algae liquid, and the best time to discharge the carbon sink algae liquid and repeat the cultivation step is 90 days.
  16. 一种权利要求3~15任一项所述的基于光合绿藻的碳汇藻液的制备方法制得的碳汇藻液。A carbon sink algae liquid prepared by the method for preparing photosynthetic green algae-based carbon sink algae liquid according to any one of claims 3 to 15.
  17. 一种如权利要求16所述的碳汇藻液的应用,其特征在于,将所述碳汇藻液均匀喷洒在辽东栎的叶面上,该碳汇藻液的浓度越高,辽东栎的光合作用越强、碳汇量增加。An application of the carbon sequestration algae liquid as claimed in claim 16, characterized in that, the carbon sequestration algae liquid is evenly sprayed on the leaf surface of Quercus liaotungensis, the higher the concentration of the carbon sequestration algae liquid is, the higher the concentration of the carbon sequestration algae liquid is. The stronger the photosynthesis, the higher the carbon sink.
  18. 一种如权利要求16所述的碳汇藻液的应用,其特征在于,将所述碳汇藻液均匀喷洒在山楂树的叶面上,该碳汇藻液的浓度越高,山楂树的光合作用越强、碳汇量增加,成熟山楂的糖度提高、不饱和脂肪酸的含量增加。An application of the carbon sequestration algae liquid as claimed in claim 16, characterized in that the carbon sequestration algae liquid is evenly sprayed on the leaf surface of the hawthorn tree, the higher the concentration of the carbon sequestration algae liquid, the greater the yield of the hawthorn tree. The stronger the photosynthesis, the higher the carbon sink, the higher the sugar content and the unsaturated fatty acid content of mature hawthorn.
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