CN113337434A - Microbial agent for treating high-salinity wastewater and preparation method thereof - Google Patents

Microbial agent for treating high-salinity wastewater and preparation method thereof Download PDF

Info

Publication number
CN113337434A
CN113337434A CN202110636664.7A CN202110636664A CN113337434A CN 113337434 A CN113337434 A CN 113337434A CN 202110636664 A CN202110636664 A CN 202110636664A CN 113337434 A CN113337434 A CN 113337434A
Authority
CN
China
Prior art keywords
culture medium
lactobacillus
pseudomonas stutzeri
bacillus subtilis
salinity wastewater
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Withdrawn
Application number
CN202110636664.7A
Other languages
Chinese (zh)
Inventor
戴威
赵敏
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to CN202110636664.7A priority Critical patent/CN113337434A/en
Publication of CN113337434A publication Critical patent/CN113337434A/en
Withdrawn legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12NMICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
    • C12N1/00Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
    • C12N1/20Bacteria; Culture media therefor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C02F3/341Consortia of bacteria
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C02F3/347Use of yeasts or fungi
    • 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
    • C12N1/14Fungi; Culture media therefor
    • C12N1/16Yeasts; Culture media therefor
    • 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
    • C12N1/36Adaptation or attenuation of cells
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/101Sulfur compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/12Halogens or halogen-containing compounds

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Organic Chemistry (AREA)
  • Microbiology (AREA)
  • Biotechnology (AREA)
  • Zoology (AREA)
  • Wood Science & Technology (AREA)
  • Genetics & Genomics (AREA)
  • Bioinformatics & Cheminformatics (AREA)
  • Medicinal Chemistry (AREA)
  • Biochemistry (AREA)
  • Tropical Medicine & Parasitology (AREA)
  • Virology (AREA)
  • Mycology (AREA)
  • Biomedical Technology (AREA)
  • General Health & Medical Sciences (AREA)
  • General Engineering & Computer Science (AREA)
  • Water Supply & Treatment (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Cell Biology (AREA)
  • Botany (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

The invention relates to a microbial agent for treating high-salinity wastewater and a preparation method thereof, wherein the active ingredients of the microbial agent for treating the high-salinity wastewater comprise: the bacillus licheniformis, the bacillus subtilis, the microzyme, the lactobacillus and the pseudomonas stutzeri have the effective viable count ratio of 8: 2: 3: 3: 1; according to the invention, the bacillus licheniformis, the bacillus subtilis, the saccharomycetes, the lactobacillus and the pseudomonas stutzeri are acclimated to adapt to a high-salt environment, no protective agent is required to be added, and the high-salt environment cannot be inhibited or even poisoned by high salinity, so that the biomass is reduced, and the treatment efficiency of high-salt wastewater is reduced; and then, the bacillus licheniformis, the bacillus subtilis, the saccharomycetes, the lactobacillus and the pseudomonas stutzeri are used for synergistically removing organic matters, SS, ammonia nitrogen and salts in the high wastewater, so that the removal efficiency of TOC is improved.

Description

Microbial agent for treating high-salinity wastewater and preparation method thereof
Technical Field
The invention relates to the field of industrial wastewater biochemical treatment, in particular to a microbial agent for treating high-salinity wastewater and a preparation method thereof.
Background
The high-salinity wastewater refers to total salt (such as Na)+、K+、ClAnd SO4 2-Etc.) waste water with the mass fraction more than or equal to 1 percent. In recent years, direct utilization of seawater (such as seawater used for flushing toilets, roads, fire fighting and industrial cooling water) is actively developed in coastal cities, and in 2020, the direct utilization amount of seawater in China reaches 1 × 109m3·a-1The rapid increase in the amount of direct seawater use is a significant cause of the large discharge of high salinity wastewater. At present, the most main treatment mode of high-salinity wastewater is to enter a municipal sewage treatment system through a municipal pipe network. High salinity wastewater typically contains Na+、K+、ClAnd SO4 2-And the like, and the high concentration of the ions can quickly increase the osmotic pressure of cells to destroy the somatic cells, and simultaneously produce salting-out action to reduce the activity of dehydrogenase to inhibit the growth of bacteria, and the high concentration of chloride ions has certain toxic action on the bacteria. Therefore, the high-salinity wastewater can generate obvious inhibiting effect on the traditional biological sewage treatment process, and particularly in the starting period of the biological sewage treatment process, the inhibition of the activated sludge can cause the quality deterioration of process effluent and the sharp increase of COD and SS concentration; the biggest problem of the biological process for treating the high-salinity wastewater is that the metabolic function of microorganisms is damaged, the number of primary and secondary animals is greatly reduced, and the removal efficiency of TOC is low.
Disclosure of Invention
The invention aims to overcome the defects of the prior art and provide a microbial agent for treating high-salinity wastewater and a preparation method thereof, so that the removal efficiency of TOC is greatly improved.
The purpose of the invention is realized by the following technical scheme: the microbial agent for treating the high-salinity wastewater comprises active ingredients, wherein the active ingredients comprise: the bacillus licheniformis, the bacillus subtilis, the microzyme, the lactobacillus and the pseudomonas stutzeri have the effective viable count ratio of 8: 2: 3: 3: 1.
further, the total effective viable count of the active ingredients is 1 × 1010-1×1012CFU/ml。
Further, the microbial inoculum also comprises a culture medium mixed with the active ingredients, and the volume of the microbial inoculum is 1-3% of the volume of the culture medium.
Furthermore, the formula of the culture medium is 30-40g of glucose, 10-16g of tryptone, 50-63g of sodium chloride, 15-18g of agar and 4-8gKH2PO4And 1L of water.
The preparation method of the microbial agent for treating the high-salinity wastewater comprises the following steps
S1: respectively culturing the domesticated bacillus licheniformis, bacillus subtilis, saccharomycetes, lactobacillus and pseudomonas stutzeri to a plateau stage;
s2: preparing the culture medium, uniformly mixing the raw materials for preparing the culture medium according to a proportion, adjusting the pH value to be 6.0-7.2, sterilizing at the temperature of 110-;
s3: uniformly mixing the bacillus licheniformis, the bacillus subtilis, the yeast, the lactobacillus and the pseudomonas stutzeri which are cultured to a plateau stage according to a proportion, then adding the mixture into the culture medium at 37 ℃, wherein the volume of the microbial inoculum is 1-3% of the volume of the culture medium, and culturing for 68-75h after uniform mixing.
The acclimatization step comprises the steps of respectively putting the bacillus licheniformis, the bacillus subtilis, the microzyme, the lactobacillus and the pseudomonas stutzeri into LB liquid culture medium with the salinity of 6 percent, and carrying out acclimatization at the temperature of 25 ℃ and at the temperature of 150 r.min-1Cultured under the conditions of (1), and OD was measured every 2 hours600When OD of the strain600Respectively inoculating strains 1 to LB liquid culture medium with salinity of 8% at 25 deg.C and 150r min to obtain strains 1 respectively-1Under the conditions ofCulturing, determining OD every 2h600When OD of the strain600When the values respectively reach 1.2-1.6, the domesticated bacillus licheniformis, bacillus subtilis, saccharomycete, lactobacillus and pseudomonas stutzeri are obtained.
According to the invention, the bacillus licheniformis, the bacillus subtilis, the saccharomycetes, the lactobacillus and the pseudomonas stutzeri are acclimated to adapt to a high-salt environment, no protective agent is required to be added, and the high-salt environment cannot be inhibited or even poisoned by high salinity, so that the biomass is reduced, and the treatment efficiency of high-salt wastewater is reduced; and then, the bacillus licheniformis, the bacillus subtilis, the saccharomycetes, the lactobacillus and the pseudomonas stutzeri are used for synergistically removing organic matters, SS, ammonia nitrogen and salts in the high wastewater, so that the removal efficiency of TOC is improved.
Further, the formula of the LB liquid culture medium is tryptone 10g, NaCl50g, agar 15g, glucose 20g and water 1L.
Further, the inoculation amounts of the bacillus licheniformis, the bacillus subtilis, the yeast, the lactobacillus and the pseudomonas stutzeri are all 1.2-3.3% of the volume of the LB liquid culture medium.
The invention has the following advantages: no protective agent is added, and active ingredients in the microbial inoculum are not damaged in a high-salt environment, so that the high-salt wastewater treatment efficiency is reduced; meanwhile, the TOC treatment efficiency of the high-salinity wastewater is improved under the synergistic effect of the bacillus licheniformis, the bacillus subtilis, the saccharomycetes, the lactobacillus and the pseudomonas stutzeri; and the application range is wide, and the method is suitable for both aerobic environment and anaerobic environment.
Detailed Description
Reference will now be made in detail to various exemplary embodiments of the invention, the detailed description should not be construed as limiting the invention but as a more detailed description of certain aspects, features and embodiments of the invention.
Example 1
The preparation method of the microbial agent for treating the high-salinity wastewater comprises the following steps
S11: the bacillus licheniformis and the bacillus subtilis are mixedThe yeast, the lactobacillus and the pseudomonas stutzeri are respectively put into an LB liquid culture medium with the salinity of 6% (the formula of the LB liquid culture medium comprises 10g of tryptone, 50g of NaCl, 15g of agar, 20g of glucose and 1L of water), and the inoculation amounts of the bacillus licheniformis, the bacillus subtilis, the yeast, the lactobacillus and the pseudomonas stutzeri are respectively 1.2% of the volume of the LB liquid culture medium; at 25 deg.C and 150r min-1Cultured under the conditions of (1), and OD was measured every 2 hours600When OD of the strain600Respectively inoculating strains 1 with salt content of 8% in LB liquid culture medium at 25 deg.C and 150r min to obtain strains 1-1Cultured under the conditions of (1), and OD was measured every 2 hours600When OD of the strain600When the values respectively reach 1.2, obtaining the domesticated bacillus licheniformis, bacillus subtilis, saccharomycetes, lactobacillus and pseudomonas stutzeri;
s12: respectively culturing the domesticated bacillus licheniformis, bacillus subtilis, saccharomycetes, lactobacillus and pseudomonas stutzeri to a plateau stage;
s2: preparing the culture medium by mixing glucose 30g, tryptone 10g, sodium chloride 50g, agar 15g, 4gKH2PO4Uniformly mixing the raw materials of 1L of water for preparing the culture medium, adjusting the pH value to 6.0, sterilizing at 110 ℃ for 18min, and cooling to 37 ℃;
s3: and (3) culturing the bacillus licheniformis, the bacillus subtilis, the microzyme, the lactobacillus and the pseudomonas stutzeri which are cultured to a plateau stage according to the effective viable bacteria ratio of 8: 2: 3: 3: 1, uniformly mixing, and controlling the total effective viable count of the active ingredients to be 1 multiplied by 1010CFU/ml, then adding the mixture into the culture medium at 37 ℃, wherein the inoculation amount of the effective viable bacteria is 1 percent of the volume of the culture medium, and culturing for 68 hours after uniformly mixing.
Example 2
The preparation method of the microbial agent for treating the high-salinity wastewater comprises the following steps
S11: respectively putting the bacillus licheniformis, the bacillus subtilis, the microzyme, the lactobacillus and the pseudomonas stutzeri into an LB liquid culture medium with the salinity of 6 percent (the LBThe formula of the liquid culture medium comprises 10g of tryptone, 50g of NaCl50g, 15g of agar, 20g of glucose and 1L of water, wherein the inoculation amounts of the bacillus licheniformis, the bacillus subtilis, the yeast, the lactobacillus and the pseudomonas stutzeri are respectively 2.3 percent of the volume of the LB liquid culture medium; at 25 deg.C and 150r min-1Cultured under the conditions of (1), and OD was measured every 2 hours600When OD of the strain600When the values respectively reach 0.6, obtaining strains 1, respectively inoculating the strains 1 into LB liquid culture medium with salinity of 8%, at 25 deg.C and 150 r.min-1Cultured under the conditions of (1), and OD was measured every 2 hours600When OD of the strain600When the values respectively reach 1.5, obtaining the domesticated bacillus licheniformis, bacillus subtilis, saccharomycetes, lactobacillus and pseudomonas stutzeri;
s12: respectively culturing the domesticated bacillus licheniformis, bacillus subtilis, saccharomycetes, lactobacillus and pseudomonas stutzeri to a plateau stage;
s2: preparing the culture medium by mixing 37g of glucose, 13g of tryptone, 57g of sodium chloride, 16g of agar and 7gKH2PO4Uniformly mixing the raw materials of 1L of water for preparing the culture medium, adjusting the pH value to 6.8, sterilizing at 114 ℃ for 23min, and cooling to 37 ℃;
s3: and (3) culturing the bacillus licheniformis, the bacillus subtilis, the microzyme, the lactobacillus and the pseudomonas stutzeri which are cultured to a plateau stage according to the effective viable bacteria ratio of 8: 2: 3: 3: 1, uniformly mixing, and controlling the total effective viable count of the active ingredients to be 1 multiplied by 1011CFU/ml, then adding the mixture into the culture medium at 37 ℃, wherein the inoculation amount of the effective viable bacteria is 2% of the volume of the culture medium, and uniformly mixing and culturing for 72 hours.
Example 3
The preparation method of the microbial agent for treating the high-salinity wastewater comprises the following steps
S11: respectively putting the bacillus licheniformis, the bacillus subtilis, the microzyme, the lactobacillus and the pseudomonas stutzeri into an LB liquid culture medium with the salinity of 6% (the formula of the LB liquid culture medium comprises 10g of tryptone, 50g of NaCl, 50g, 15g of agar, 20g of glucose and 1L of water), and putting the bacillus licheniformis, the bacillus subtilis, the microzyme, the lactobacillus and the pseudomonas stutzeri into the LB liquid culture medium with the salinity of 6% (the formula of the LB liquid culture medium comprises 10g of tryptone, 50g of NaCl, g, 15g of agar, 20g of glucose and 1L of water)The inoculation amounts of bacillus, bacillus subtilis, yeast, lactobacillus and pseudomonas stutzeri are respectively 3.3 percent of the volume of the LB liquid culture medium; at 25 deg.C and 150r min-1Cultured under the conditions of (1), and OD was measured every 2 hours600When OD of the strain600When the values respectively reach 0.7, obtaining strains 1, respectively inoculating the strains 1 into LB liquid culture medium with salinity of 8%, at 25 deg.C and 150r min-1Cultured under the conditions of (1), and OD was measured every 2 hours600When OD of the strain600When the values respectively reach 1.6, obtaining the domesticated bacillus licheniformis, bacillus subtilis, saccharomycetes, lactobacillus and pseudomonas stutzeri;
s12: respectively culturing the domesticated bacillus licheniformis, bacillus subtilis, saccharomycetes, lactobacillus and pseudomonas stutzeri to a plateau stage;
s2: preparing the culture medium by mixing glucose 40g, tryptone 16g, sodium chloride 63g, agar 18g, 4-8gKH2PO4Uniformly mixing the raw materials of 1L of water for preparing the culture medium, adjusting the pH value to 7.2, sterilizing at 118 ℃ for 27min, and cooling to 37 ℃;
s3: and (3) culturing the bacillus licheniformis, the bacillus subtilis, the microzyme, the lactobacillus and the pseudomonas stutzeri which are cultured to a plateau stage according to the effective viable bacteria ratio of 8: 2: 3: 3: 1, uniformly mixing, and controlling the total effective viable count of the active ingredients to be 1 multiplied by 1012CFU/ml, then adding the mixture into the culture medium at 37 ℃, wherein the inoculation amount of the effective viable bacteria is 3% of the volume of the culture medium, and uniformly mixing and culturing for 75 h.
Comparative example 1:
the conventional microbial agent for treating high-salinity wastewater on the market is purchased, the same amount of high-salinity wastewater is treated by the microbial agent prepared in the comparative examples 1-3, the TOC removal rate of the treated high-salinity wastewater is detected, and the experimental data are shown in Table 1.
Comparative example 2:
after the existing microbial agent for treating high-salinity wastewater on the market, which is the same as that of the microbial agent for treating high-salinity wastewater in the comparative example 1, is purchased for acclimatization treatment, the same amount of high-salinity wastewater is treated by the microbial agent prepared in the comparative examples 1-3, the TOC removal rate of the treated high-salinity wastewater is detected, and the experimental data are shown in Table 1
Table 1: TOC value recording table
Example 1 Example 2 Example 3 Comparative example 1 Comparative example 2
TOC removal (%) 94.6 98.7 90.2 73.5 89.1
As shown in Table 1, the microbial agent for treating high-salinity wastewater has higher TOC removal efficiency of the high-salinity wastewater, which can reach 98.7% at most, compared with the existing microbial agent on the market.
The present invention is not limited to the above-described embodiments, and any variations, modifications, and substitutions which may occur to those skilled in the art may be made without departing from the spirit of the invention.

Claims (8)

1. The microbial agent for treating the high-salinity wastewater comprises active ingredients, and is characterized in that the active ingredients comprise: the bacillus licheniformis, the bacillus subtilis, the microzyme, the lactobacillus and the pseudomonas stutzeri have the effective viable count ratio of 8: 2: 3: 3: 1.
2. the microbial agent for treating high-salinity wastewater according to claim 1, wherein the total effective viable count of the active ingredients is 1 x 1010-1×1012CFU/ml。
3. The microbial inoculant for the treatment of high-salinity wastewater of claim 1, wherein: the microbial inoculum also comprises a culture medium mixed with the active ingredients, and the volume of the microbial inoculum is 1-3% of the volume of the culture medium.
4. The microbial inoculant for the treatment of high-salinity wastewater of claim 3, wherein: the formula of the culture medium comprises 30-40g of glucose, 10-16g of tryptone, 50-63g of sodium chloride, 15-18g of agar and 4-8gKH2PO4And 1L of water.
5. The method for preparing a microbial agent for treating high-salinity wastewater according to claim 1, characterized by comprising the following steps
S1: respectively culturing the domesticated bacillus licheniformis, bacillus subtilis, saccharomycetes, lactobacillus and pseudomonas stutzeri to a plateau stage;
s2: preparing the culture medium, uniformly mixing the raw materials for preparing the culture medium according to a proportion, adjusting the pH value to be 6.0-7.2, sterilizing at the temperature of 110-;
s3: uniformly mixing the bacillus licheniformis, the bacillus subtilis, the yeast, the lactobacillus and the pseudomonas stutzeri which are cultured to a plateau stage according to a proportion, then adding the mixture into the culture medium at 37 ℃, wherein the volume of the microbial inoculum is 1-3% of the volume of the culture medium, and culturing for 68-75h after uniform mixing.
6. The method of claim 1, wherein the acclimating step comprises respectively placing the Bacillus licheniformis, Bacillus subtilis, yeast, Lactobacillus, and Pseudomonas stutzeri in LB liquid medium with a salinity of 6%, and culturing at 25 deg.C and 150 r-min-1Cultured under the conditions of (1), and OD was measured every 2 hours600When OD of the strain600Respectively inoculating strains 1 to LB liquid culture medium with salinity of 8% at 25 deg.C and 150r min to obtain strains 1 respectively-1Cultured under the conditions of (1), and OD was measured every 2 hours600When OD of the strain600When the values respectively reach 1.2-1.6, the domesticated bacillus licheniformis, bacillus subtilis, saccharomycete, lactobacillus and pseudomonas stutzeri are respectively obtained.
7. The method for preparing a microbial inoculant for treating high-salinity wastewater according to claim 6, wherein the microbial inoculant comprises: the LB liquid medium comprises 10g of tryptone, 50g of NaCl50g, 15g of agar, 20g of glucose and 1L of water.
8. The method for preparing a microbial inoculant for treating high-salinity wastewater according to claim 6, wherein the microbial inoculant comprises: during acclimation, the inoculation amounts of the bacillus licheniformis, the bacillus subtilis, the saccharomycetes, the lactobacillus and the pseudomonas stutzeri are all 1.2-3.3% of the volume of the LB liquid culture medium.
CN202110636664.7A 2021-06-08 2021-06-08 Microbial agent for treating high-salinity wastewater and preparation method thereof Withdrawn CN113337434A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202110636664.7A CN113337434A (en) 2021-06-08 2021-06-08 Microbial agent for treating high-salinity wastewater and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202110636664.7A CN113337434A (en) 2021-06-08 2021-06-08 Microbial agent for treating high-salinity wastewater and preparation method thereof

Publications (1)

Publication Number Publication Date
CN113337434A true CN113337434A (en) 2021-09-03

Family

ID=77475191

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202110636664.7A Withdrawn CN113337434A (en) 2021-06-08 2021-06-08 Microbial agent for treating high-salinity wastewater and preparation method thereof

Country Status (1)

Country Link
CN (1) CN113337434A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN117904011A (en) * 2024-03-20 2024-04-19 江苏省环境工程技术有限公司 Microbial agent for treating high-salt refractory industrial wastewater and preparation method and application thereof

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN117904011A (en) * 2024-03-20 2024-04-19 江苏省环境工程技术有限公司 Microbial agent for treating high-salt refractory industrial wastewater and preparation method and application thereof
CN117904011B (en) * 2024-03-20 2024-05-28 江苏省环境工程技术有限公司 Microbial agent for treating high-salt refractory industrial wastewater and preparation method and application thereof

Similar Documents

Publication Publication Date Title
CN108118022B (en) Microbial culture promoter for completing denitrification process and application thereof
CN107400649B (en) Composite microbial inoculum, preparation method and application thereof, and sludge treatment method for black and odorous riverway
CN106635861B (en) A kind of de- COD denitrification microorganism microbial inoculum of salt tolerant and preparation method thereof
CN109678246B (en) Method suitable for treating water bloom in lakes and reservoirs and slow flow type riverways
CN104694443A (en) Improved biological microbial agent for disposing industrial sewage and preparation method and application thereof
CN108117165B (en) Method for treating ammonia-containing wastewater
CN105645710A (en) Method for sludge reduction by using compound microbial preparation
CN101955885A (en) High-efficiency denitrification mixed bacterial agent and application thereof
CN107236687B (en) Pseudomonas stutzeri with hexavalent chromium removal and aerobic denitrification performance and application thereof
CN113604397B (en) High-salt degradation-resistant waste water COD (chemical oxygen demand) strain, screening method and application
Curtis Bacterial pathogen removal in wastewater treatment plants
CN104611279B (en) A kind of red city Rhodococcus sp LH N13 and its microbial bacterial agent and purposes
CN113337434A (en) Microbial agent for treating high-salinity wastewater and preparation method thereof
CN105585133A (en) Bio-denitrification method for high-salt-content wastewater discharged from catalyst production process
CN112723536B (en) Method for retarding membrane pollution by utilizing quorum sensing inhibitor furanone in municipal sewage treatment process based on anaerobic membrane bioreactor
CN110408565A (en) A kind of efficient denitrification composite bacteria agent, preparation and its application
CN110317752B (en) Denitrifying microbial inoculum and using method thereof
CN110938557A (en) Composite microbial inoculum for degrading COD (chemical oxygen demand) in wastewater and preparation method thereof
CN111286478A (en) Grease degradation composite bacterial agent and preparation method and application thereof
CN108118008A (en) Microbial bacterial agent of Efficient salt-tolerant and its preparation method and application
CN106745815A (en) It is a kind of to improve the water treatment agent that biochemical system goes ammonia nitrogen ability
CN111073869A (en) Composite indigenous microorganism domestication enzyme for efficiently improving urban black and odorous water body and method for treating urban black and odorous water body
WO2020097994A1 (en) Sphingobacterium having both heterotrophic nitrification and aerobic denitrification functions and application thereof
CN110683655A (en) Underwater bacterium distribution process for eliminating black and odorous river channel
CN106399200B (en) Alcaligenes and application thereof in high-salt high-polymer wastewater

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
WW01 Invention patent application withdrawn after publication

Application publication date: 20210903

WW01 Invention patent application withdrawn after publication