CN107381945A - A kind of processing method of degumming silkworm cocoons waste water - Google Patents

A kind of processing method of degumming silkworm cocoons waste water Download PDF

Info

Publication number
CN107381945A
CN107381945A CN201710666439.1A CN201710666439A CN107381945A CN 107381945 A CN107381945 A CN 107381945A CN 201710666439 A CN201710666439 A CN 201710666439A CN 107381945 A CN107381945 A CN 107381945A
Authority
CN
China
Prior art keywords
waste water
degumming
processing method
silkworm cocoons
mass concentration
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201710666439.1A
Other languages
Chinese (zh)
Inventor
王洪喜
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.)
HEFEI JUFENG THROWING CO Ltd
Original Assignee
HEFEI JUFENG THROWING CO Ltd
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 HEFEI JUFENG THROWING CO Ltd filed Critical HEFEI JUFENG THROWING CO Ltd
Priority to CN201710666439.1A priority Critical patent/CN107381945A/en
Publication of CN107381945A publication Critical patent/CN107381945A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/30Nature of the water, waste water, sewage or sludge to be treated from the textile industry
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions
    • 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
    • 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
    • C02F3/342Biological treatment of water, waste water, or sewage characterised by the microorganisms used characterised by the enzymes used

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)

Abstract

The invention mainly relates to silk processing technique field, discloses a kind of processing method of degumming silkworm cocoons waste water, including:Acid-base accommodation, enzymolysis, one time fermentation, secondary fermentation, discharge;Method is simple, easy to operation, without special instrument and equipment, is easy to promote, and the protein removal rate in degumming waste water is reached 97.3%, fatty clearance reaches 98.1%, hence it is evident that reduces the macromolecular nutrition in degumming waste water, environmental protection, solves the energy;Containing substantial amounts of acid or alkali in degumming waste water, after pH-value is adjusted, degumming waste water is reduced soda acid excitant, beneficial to post-processing, improve treatment effect;Complex enzyme is first added after pH-value regulation to be digested, the fat and pectin composition of macromolecular in Decomposition Wastewater, substantial amounts of sericin in proteases for decomposing waste water is added, avoids the oxidation and the substantial amounts of dissolved oxygen of decomposition and consumption, mitigation environment and water pollution of fat and protein after discharge of wastewater.

Description

A kind of processing method of degumming silkworm cocoons waste water
Technical field
The invention mainly relates to silk processing technique field, more particularly to a kind of processing method of degumming silkworm cocoons waste water.
Background technology
Silk is most light most soft most thin natural fiber in nature, is one of earliest animal origin of human use, matter Light and elongated, fabric sheen is good, comfortable and easy to wear, and feel is smooth plentiful, and poor heat conductivity, moisture absorption is breathed freely, for knit the various silks and satins of system and Knitwear, and for industry, national defence and medicine and other fields;After silkworm cocoons, silk cocoon is prepared into silk needs to carry out degumming Journey, waste water caused by now widely used degumming silkworm cocoons method all contain a large amount of protein, aliphatic acid or alkali, and flowing into river course will Oxygen in water can be largely consumed, water body is lost self-purification capacity, causes environmental pollution and substantial amounts of energy waste, therefore, is needed Want a kind of processing method of degumming silkworm cocoons waste water.
The content of the invention
The defects of in order to make up prior art, it is an object of the invention to provide a kind of processing method of degumming silkworm cocoons waste water.
A kind of processing method of degumming silkworm cocoons waste water, comprises the following steps:
(1)Acid-base accommodation:Degumming waste water progress pH is adjusted to 5.3 ~ 5.6, degumming waste water is reduced soda acid excitant, after being beneficial to Phase is handled, and is improved treatment effect, is obtained acid-base accommodation waste water;
(2)Enzymolysis:Complex enzyme is added into acid-base accommodation waste water, it is 0.04 ~ 0.06% to make mass concentration, and stirring enzymolysis 2 ~ 3 is small When, protease is added, continues enzymolysis 4 ~ 5 hours, first adds the fat and pectin composition of macromolecular in complex enzyme Decomposition Wastewater, then Substantial amounts of sericin in proteases for decomposing waste water is added, avoids fatty and protein oxidation and decomposition and consumption after discharge of wastewater Substantial amounts of dissolved oxygen, mitigate environment and water pollution, obtain enzymolysis waste water;
(3)One time fermentation:Sodium selenite is added into enzymolysis waste water, suppresses wastewater oxidation, increases the mineral element in waste water, profit In later stage microbial growth, it is 0.05 ~ 0.07% to make mass concentration, and lactic acid bacteria is accessed after well mixed, in 34 ~ 36 DEG C of fermentations 2 ~ 3 My god, promote a large amount of Extracellular metabolisms caused by growing microorganism to promote growing microorganism using the nutritional ingredient in waste water, profit Grown in plant and animal, obtain one time fermentation waste water;
(4)Secondary fermentation:EM bacterium are accessed into one time fermentation waste water, it is 4 ~ 6% to make mass concentration, is fermented 7 ~ 9 days in 24 ~ 28 DEG C, Beneficial microbe colony in abundant waste water, a large amount of organic principles in waste water are fully converted, is easy to recycle after discharge, keeps away Exempt from the pollution to environment and river, obtain secondary fermentation waste water;
(5)Discharge:By secondary fermentation waste water through 60 ~ 80 mesh screens, waste discharge is obtained.
The step(1)PH regulations, using solution be sodium carbonate liquor that mass concentration is 5 ~ 7% or volume fraction is 3 ~ 4% acetum.
The step(2)Complex enzyme, be made up of lipase and pectase, the weight ratio of lipase and pectase for 10 ~ 12:1。
The step(2)Protease, be bromelain, mass concentration is 0.07 ~ 0.09%.
The step(3)Lactic acid bacteria, mass concentration be 3 ~ 5%, be made up of the bacterial strain of following parts by weight:Lactobacillus acidophilus 17 ~ 19, streptococcus thermophilus 12 ~ 14, Lactobacillus plantarum 7 ~ 9, Bu Shi lactobacillus 4 ~ 6, each bacterial strain pass through re-activation.
The waste discharge that a kind of processing method of the degumming silkworm cocoons waste water is prepared.
The application method of the waste discharge, can be used as nutrient solution be used for plant irrigation, animal drink, aquaculture or work It is direct discharging of waste water in river.
It is an advantage of the invention that:The processing method of degumming silkworm cocoons waste water provided by the invention, method is simple, easy to operation, Without special instrument and equipment, it is easy to promote, the protein removal rate in degumming waste water is reached 97.3%, fatty clearance Reach 98.1%, hence it is evident that reduce the macromolecular nutrition in degumming waste water, environmental protection, solve the energy;Containing a large amount of in degumming waste water Acid or alkali, after pH-value is adjusted, degumming waste water is reduced soda acid excitant, beneficial to post-processing, improve treatment effect;Acid Complex enzyme is first added after base number regulation to be digested, the fat and pectin composition of macromolecular, add protease in Decomposition Wastewater Substantial amounts of sericin in Decomposition Wastewater, the oxidation of fat and protein and decomposition and consumption after discharge of wastewater is avoided largely to dissolve Oxygen, mitigate environment and water pollution;Sodium selenite is added into enzymolysis waste water, suppresses wastewater oxidation, increases the mineral in waste water Element, beneficial to later stage microbial growth, after accessing lactic acid bacteria the nutritional ingredient in waste water can be utilized to promote growing microorganism to produce A large amount of Extracellular metabolisms can promote growing microorganism, beneficial to plant and animal grow;EM bacterium are accessed again carries out secondary fermentation, Beneficial microbe colony in abundant waste water, a large amount of organic principles in waste water are fully converted, is easy to recycle after discharge, keeps away Exempt from the pollution to environment and river.
Embodiment
Illustrate the present invention with specific embodiment below.
Embodiment 1
A kind of processing method of degumming silkworm cocoons waste water, comprises the following steps:
(1)Acid-base accommodation:Degumming waste water progress pH is adjusted to 5.3 ~ 5.6, degumming waste water is reduced soda acid excitant, after being beneficial to Phase is handled, and is improved treatment effect, is obtained acid-base accommodation waste water;
(2)Enzymolysis:Complex enzyme is added into acid-base accommodation waste water, it is 0.04% to make mass concentration, stirring enzymolysis 2 hours, adds egg White enzyme, continues enzymolysis 4 hours, first adds the fat and pectin composition of macromolecular in complex enzyme Decomposition Wastewater, adds protease Substantial amounts of sericin in Decomposition Wastewater, the oxidation of fat and protein and decomposition and consumption after discharge of wastewater is avoided largely to dissolve Oxygen, mitigate environment and water pollution, obtain enzymolysis waste water;
(3)One time fermentation:Sodium selenite is added into enzymolysis waste water, suppresses wastewater oxidation, increases the mineral element in waste water, profit In later stage microbial growth, it is 0.05% to make mass concentration, and lactic acid bacteria is accessed after well mixed, is fermented 2 days in 34 DEG C, using useless Nutritional ingredient in water promotes a large amount of Extracellular metabolisms caused by growing microorganism to promote growing microorganism, beneficial to plant and moves Thing grows, and obtains one time fermentation waste water;
(4)Secondary fermentation:EM bacterium are accessed into one time fermentation waste water, it is 4% to make mass concentration, is fermented 7 days in 24 DEG C, is enriched useless Beneficial microbe colony in water, a large amount of organic principles in waste water are fully converted, is easy to recycle after discharge, avoids to ring Border and the pollution in river, obtain secondary fermentation waste water;
(5)Discharge:By secondary fermentation waste water through 60 ~ 80 mesh screens, waste discharge is obtained.
The step(1)PH regulations, using solution be sodium carbonate liquor that mass concentration is 5% or volume fraction is 3% Acetum.
The step(2)Complex enzyme, be made up of lipase and pectase, the weight ratio of lipase and pectase is 10: 1。
The step(2)Protease, be bromelain, mass concentration 0.07%.
The step(3)Lactic acid bacteria, mass concentration 3%, be made up of the bacterial strain of following parts by weight:Lactobacillus acidophilus 17, Streptococcus thermophilus 12, Lactobacillus plantarum 7, Bu Shi lactobacillus 4, each bacterial strain pass through re-activation.
The waste discharge that a kind of processing method of the degumming silkworm cocoons waste water is prepared.
The application method of the waste discharge, can be used as nutrient solution be used for plant irrigation, animal drink, aquaculture or work It is direct discharging of waste water in river.
Embodiment 2
A kind of processing method of degumming silkworm cocoons waste water, comprises the following steps:
(1)Acid-base accommodation:Degumming waste water progress pH is adjusted to 5.3 ~ 5.6, degumming waste water is reduced soda acid excitant, after being beneficial to Phase is handled, and is improved treatment effect, is obtained acid-base accommodation waste water;
(2)Enzymolysis:Complex enzyme is added into acid-base accommodation waste water, it is 0.05% to make mass concentration, stirring enzymolysis 2 hours, adds egg White enzyme, continues enzymolysis 4 hours, first adds the fat and pectin composition of macromolecular in complex enzyme Decomposition Wastewater, adds protease Substantial amounts of sericin in Decomposition Wastewater, the oxidation of fat and protein and decomposition and consumption after discharge of wastewater is avoided largely to dissolve Oxygen, mitigate environment and water pollution, obtain enzymolysis waste water;
(3)One time fermentation:Sodium selenite is added into enzymolysis waste water, suppresses wastewater oxidation, increases the mineral element in waste water, profit In later stage microbial growth, it is 0.06% to make mass concentration, and lactic acid bacteria is accessed after well mixed, is fermented 2 days in 35 DEG C, using useless Nutritional ingredient in water promotes a large amount of Extracellular metabolisms caused by growing microorganism to promote growing microorganism, beneficial to plant and moves Thing grows, and obtains one time fermentation waste water;
(4)Secondary fermentation:EM bacterium are accessed into one time fermentation waste water, it is 5% to make mass concentration, is fermented 8 days in 26 DEG C, is enriched useless Beneficial microbe colony in water, a large amount of organic principles in waste water are fully converted, is easy to recycle after discharge, avoids to ring Border and the pollution in river, obtain secondary fermentation waste water;
(5)Discharge:By secondary fermentation waste water through 60 ~ 80 mesh screens, waste discharge is obtained.
The step(1)PH regulations, using solution be sodium carbonate liquor that mass concentration is 6% or volume fraction is 3% Acetum.
The step(2)Complex enzyme, be made up of lipase and pectase, the weight ratio of lipase and pectase is 11: 1。
The step(2)Protease, be bromelain, mass concentration 0.08%.
The step(3)Lactic acid bacteria, mass concentration 4%, be made up of the bacterial strain of following parts by weight:Lactobacillus acidophilus 18, Streptococcus thermophilus 13, Lactobacillus plantarum 8, Bu Shi lactobacillus 5, each bacterial strain pass through re-activation.
The waste discharge that a kind of processing method of the degumming silkworm cocoons waste water is prepared.
The application method of the waste discharge, can be used as nutrient solution be used for plant irrigation, animal drink, aquaculture or work It is direct discharging of waste water in river.
Embodiment 3
A kind of processing method of degumming silkworm cocoons waste water, comprises the following steps:
(1)Acid-base accommodation:Degumming waste water progress pH is adjusted to 5.3 ~ 5.6, degumming waste water is reduced soda acid excitant, after being beneficial to Phase is handled, and is improved treatment effect, is obtained acid-base accommodation waste water;
(2)Enzymolysis:Complex enzyme is added into acid-base accommodation waste water, it is 0.06% to make mass concentration, stirring enzymolysis 3 hours, adds egg White enzyme, continues enzymolysis 5 hours, first adds the fat and pectin composition of macromolecular in complex enzyme Decomposition Wastewater, adds protease Substantial amounts of sericin in Decomposition Wastewater, the oxidation of fat and protein and decomposition and consumption after discharge of wastewater is avoided largely to dissolve Oxygen, mitigate environment and water pollution, obtain enzymolysis waste water;
(3)One time fermentation:Sodium selenite is added into enzymolysis waste water, suppresses wastewater oxidation, increases the mineral element in waste water, profit In later stage microbial growth, it is 0.07% to make mass concentration, and lactic acid bacteria is accessed after well mixed, is fermented 3 days in 36 DEG C, using useless Nutritional ingredient in water promotes a large amount of Extracellular metabolisms caused by growing microorganism to promote growing microorganism, beneficial to plant and moves Thing grows, and obtains one time fermentation waste water;
(4)Secondary fermentation:EM bacterium are accessed into one time fermentation waste water, it is 6% to make mass concentration, is fermented 9 days in 28 DEG C, is enriched useless Beneficial microbe colony in water, a large amount of organic principles in waste water are fully converted, is easy to recycle after discharge, avoids to ring Border and the pollution in river, obtain secondary fermentation waste water;
(5)Discharge:By secondary fermentation waste water through 60 ~ 80 mesh screens, waste discharge is obtained.
The step(1)PH regulations, using solution be sodium carbonate liquor that mass concentration is 7% or volume fraction is 4% Acetum.
The step(2)Complex enzyme, be made up of lipase and pectase, the weight ratio of lipase and pectase is 12: 1。
The step(2)Protease, be bromelain, mass concentration 0.09%.
The step(3)Lactic acid bacteria, mass concentration 5%, be made up of the bacterial strain of following parts by weight:Lactobacillus acidophilus 19, Streptococcus thermophilus 14, Lactobacillus plantarum 9, Bu Shi lactobacillus 6, each bacterial strain pass through re-activation.
The waste discharge that a kind of processing method of the degumming silkworm cocoons waste water is prepared.
The application method of the waste discharge, can be used as nutrient solution be used for plant irrigation, animal drink, aquaculture or work It is direct discharging of waste water in river.
Comparative example 1
Removal step(1), remaining method, with embodiment 1.
Comparative example 2
Removal step(2)In complex enzyme, remaining method, with embodiment 1.
Comparative example 3
Removal step(2)In protease, remaining method, with embodiment 1.
Comparative example 4
Removal step(3)In sodium selenite, remaining method, with embodiment 1.
Comparative example 5
Removal step(3)In lactic acid bacteria, remaining method, with embodiment 1.
Comparative example 6
Removal step(4)In EM bacterium, remaining method, with embodiment 1.
The treatment effect of embodiment and comparative example degumming silkworm cocoons method of wastewater treatment:
Randomly select with a batch of degumming silkworm cocoons waste water 100L, be randomly divided into 10 groups, it is every group of 10L, respectively embodiment group, right The waste water of ratio group and control group, embodiment group and comparative example group carries out wastewater treatment using the processing method of the group respectively, right According to group waste water without any processing, protein content, fat content, the COD of each group waste discharge are detected after the completion of processing(Change Learn oxygen demand)And BOD5(Biochemical oxygen demand (BOD)), the treatment effect of embodiment and comparative example degumming silkworm cocoons method of wastewater treatment is shown in Table 1。
Table 1:The treatment effect of embodiment and comparative example degumming silkworm cocoons method of wastewater treatment
Project Protein/(%) Fat/(%) COD/(mg/L) BOD5/(mg/L)
Embodiment 1 0.020 0.003 136 105
Embodiment 2 0.023 0.003 143 109
Embodiment 3 0.021 0.003 139 107
Comparative example 1 0.047 0.009 514 365
Comparative example 2 0.052 0.106 3859 2482
Comparative example 3 0.274 0.047 6436 3652
Comparative example 4 0.039 0.005 478 334
Comparative example 5 0.163 0.054 1635 977
Comparative example 6 0.181 0.068 3432 1143
Control group 0.752 0.182 8657 4531
Show from the result of table 1, the processing method of the degumming silkworm cocoons waste water of embodiment, the protein and fat remained in waste water is bright Show, COD few compared with comparative example and control group(COD)And BOD5(Biochemical oxygen demand (BOD))It is significantly less than comparative example and control group, Illustrating the processing method of degumming silkworm cocoons waste water provided by the invention has good treatment effect.

Claims (7)

1. a kind of processing method of degumming silkworm cocoons waste water, it is characterised in that comprise the following steps:
(1)Acid-base accommodation:Degumming waste water progress pH is adjusted to 5.3 ~ 5.6, obtains acid-base accommodation waste water;
(2)Enzymolysis:Complex enzyme is added into acid-base accommodation waste water, it is 0.04 ~ 0.06% to make mass concentration, and stirring enzymolysis 2 ~ 3 is small When, protease is added, continues enzymolysis 4 ~ 5 hours, obtains enzymolysis waste water;
(3)One time fermentation:Sodium selenite is added into enzymolysis waste water, it is 0.05 ~ 0.07% to make mass concentration, well mixed to be followed by Enter lactic acid bacteria, fermented 2 ~ 3 days in 34 ~ 36 DEG C, obtain one time fermentation waste water;
(4)Secondary fermentation:EM bacterium are accessed into one time fermentation waste water, it is 4 ~ 6% to make mass concentration, is fermented 7 ~ 9 days in 24 ~ 28 DEG C, Obtain secondary fermentation waste water;
(5)Discharge:By secondary fermentation waste water through 60 ~ 80 mesh screens, waste discharge is obtained.
2. the processing method of degumming silkworm cocoons waste water according to claim 1, it is characterised in that the step(1)PH regulation, The use of solution is the sodium carbonate liquor that mass concentration is 5 ~ 7% or the acetum that volume fraction is 3 ~ 4%.
3. the processing method of degumming silkworm cocoons waste water according to claim 1, it is characterised in that the step(2)Complex enzyme, It is made up of lipase and pectase, the weight ratio of lipase and pectase is 10 ~ 12:1.
4. the processing method of degumming silkworm cocoons waste water according to claim 1, it is characterised in that the step(2)Protease, For bromelain, mass concentration is 0.07 ~ 0.09%.
5. the processing method of degumming silkworm cocoons waste water according to claim 1, it is characterised in that the step(3)Lactic acid bacteria, Mass concentration is 3 ~ 5%, is made up of the bacterial strain of following parts by weight:Lactobacillus acidophilus 17 ~ 19, streptococcus thermophilus 12 ~ 14, plant breast Bacillus 7 ~ 9, Bu Shi lactobacillus 4 ~ 6, each bacterial strain pass through re-activation.
6. the waste discharge that a kind of processing method of any one of claim 1 ~ 5 degumming silkworm cocoons waste water is prepared.
7. the application method of waste discharge described in a kind of claim 6, it is characterised in that nutrient solution can be used as to be filled for plant Irrigate, animal is drunk, aquaculture or conduct direct discharging of waste water are in river.
CN201710666439.1A 2017-08-07 2017-08-07 A kind of processing method of degumming silkworm cocoons waste water Pending CN107381945A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710666439.1A CN107381945A (en) 2017-08-07 2017-08-07 A kind of processing method of degumming silkworm cocoons waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710666439.1A CN107381945A (en) 2017-08-07 2017-08-07 A kind of processing method of degumming silkworm cocoons waste water

Publications (1)

Publication Number Publication Date
CN107381945A true CN107381945A (en) 2017-11-24

Family

ID=60343369

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710666439.1A Pending CN107381945A (en) 2017-08-07 2017-08-07 A kind of processing method of degumming silkworm cocoons waste water

Country Status (1)

Country Link
CN (1) CN107381945A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108947679A (en) * 2018-08-17 2018-12-07 江西省峯野生物科技有限公司 A kind of microbial organic fertilizer and preparation method thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103159329A (en) * 2013-04-02 2013-06-19 江苏艾特克环境工程有限公司 Method for in-situ enhancement of microbial activity
CN103224887A (en) * 2013-05-07 2013-07-31 山东省环境保护科学研究设计院 Preparation method of microbial nutrition agent for wastewater biochemical treatment
CN106186539A (en) * 2016-08-15 2016-12-07 桂林市福泰建材有限责任公司 A kind of silk reeling wastewater processing system
CN106630281A (en) * 2016-12-26 2017-05-10 苏州柯米智能科技有限公司 Silk reeling wastewater treatment device

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103159329A (en) * 2013-04-02 2013-06-19 江苏艾特克环境工程有限公司 Method for in-situ enhancement of microbial activity
CN103224887A (en) * 2013-05-07 2013-07-31 山东省环境保护科学研究设计院 Preparation method of microbial nutrition agent for wastewater biochemical treatment
CN106186539A (en) * 2016-08-15 2016-12-07 桂林市福泰建材有限责任公司 A kind of silk reeling wastewater processing system
CN106630281A (en) * 2016-12-26 2017-05-10 苏州柯米智能科技有限公司 Silk reeling wastewater treatment device

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
刘江坚: "《整染节能减排新技术》", 31 May 2015, 中国纺织出版社 *
马放等: "《环境生物制剂的开发与应用》", 31 March 2004, 化学工业出版社 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108947679A (en) * 2018-08-17 2018-12-07 江西省峯野生物科技有限公司 A kind of microbial organic fertilizer and preparation method thereof

Similar Documents

Publication Publication Date Title
CN103667159B (en) A kind of high-density cultivation method for genus bacillus and substratum
CN100588624C (en) Microorganism renovation agent of water environment and preparation method thereof
CN103449672B (en) Treatment method and recycling method of livestock and poultry breeding wastewater and biogas slurry
CN101974434B (en) Multi-bacterium microbial compound preparations for aquaculture and preparation method thereof
CN102924134A (en) Alga microorganism fertilizer agent and preparation method thereof
CN102219310A (en) Environment-friendly composite microbial preparation, preparation thereof, and application thereof to aquaculture
CN111793575A (en) Complex microbial inoculant and application thereof in aquaculture
CN102286376A (en) Microbial inoculum for high-efficiency fermenting bed and preparation method thereof
CN109321505A (en) A kind of complex microorganism preparations adjusting aquatic livestock enteron aisle
CN107541477A (en) A kind of method using streptococcus acidi lactici fermented solution culture photosynthetic bacteria
CN103184174A (en) Production method of bacillus subtilis biological agent used for sodium humate-containing feed in medium
He et al. An integrated algal-bacterial system for the bio-conversion of wheat bran and treatment of rural domestic effluent
CN101407761A (en) Liquid inocula composed of yeast fused strain, Geotrichum candidum Link and Rhizopus, and preparation and use thereof
CN101147529A (en) Microecological preparation for aquaculture and its preparation method
CN102696916A (en) Compound fermentation method for producing fermented feed
CN105002110B (en) Complex microorganism preparations and its application in the processing of algal bloom water body
CN105886437A (en) Composition or composite bacterium agent for controlling water body pollution
CN102689990A (en) Method for controlling water quality in shrimp pool by using bacillus and bagasse
CN107381945A (en) A kind of processing method of degumming silkworm cocoons waste water
CN112725397A (en) Method for producing single-cell protein by microbial fermentation
CN106465695A (en) A kind of enhanced ecological base and preparation method thereof
CN110029066A (en) A method of utilizing beer waste water culture chlorella
CN105087417A (en) Compound microbial agent for aerobic treatment on food processing wastewater and application of compound microbial agent
CN113817635A (en) Method for culturing bacillus by using soybean whey wastewater
CN103773713B (en) There is microorganism formulation of high Biofilm Colonization efficiency and preparation method thereof

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
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20171124