CN110551663A - Aeromonas rillii preparation for treating domestic sludge and preparation method and application thereof - Google Patents
Aeromonas rillii preparation for treating domestic sludge and preparation method and application thereof Download PDFInfo
- Publication number
- CN110551663A CN110551663A CN201910928200.6A CN201910928200A CN110551663A CN 110551663 A CN110551663 A CN 110551663A CN 201910928200 A CN201910928200 A CN 201910928200A CN 110551663 A CN110551663 A CN 110551663A
- Authority
- CN
- China
- Prior art keywords
- aeromonas
- preparation
- domestic sludge
- culture medium
- culture
- 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- Withdrawn
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/02—Biological treatment
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms; 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
- C12N1/20—Bacteria; Culture media therefor
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Health & Medical Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Zoology (AREA)
- Wood Science & Technology (AREA)
- Genetics & Genomics (AREA)
- Biotechnology (AREA)
- Environmental & Geological Engineering (AREA)
- Tropical Medicine & Parasitology (AREA)
- Virology (AREA)
- Medicinal Chemistry (AREA)
- Biomedical Technology (AREA)
- Water Supply & Treatment (AREA)
- Microbiology (AREA)
- Hydrology & Water Resources (AREA)
- Molecular Biology (AREA)
- Biochemistry (AREA)
- General Engineering & Computer Science (AREA)
- General Health & Medical Sciences (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
The invention discloses an aeromonas reesei preparation for treating domestic sludge as well as a preparation method and application thereof, belonging to the technical field of domestic sludge treatment.
Description
Technical Field
The invention belongs to the technical field of domestic sludge treatment, and particularly relates to an aeromonas rillii preparation for treating domestic sludge as well as a preparation method and application thereof.
background
The treatment technology of urban domestic sludge is always an elbow stopping problem which troubles the development of cities. Along with the development of urbanization and the increasing of urban population, the discharge amount of industrial wastewater and domestic sewage is increasing day by day, the annual sewage discharge of China reaches 18 billions of cubic meters, and the sludge generated in the sewage treatment process is calculated by 0.3-0.5 percent of the sewage treatment amount, and the generation amount also reaches thousands of tons. At present, most of domestic large and medium-sized cities comprise Chengdu, Shanghai, Guangzhou, Beijing and the like face the condition of no land burying, and are one of the most outstanding problems facing city construction and environmental protection in recent years. The sludge has complex components, contains toxic, harmful and difficultly-degradable organic matters, pathogenic bacteria, parasites and heavy metals, also contains a large amount of nutrient components necessary for the growth of plants, and has good yield-increasing effect on the growth of crops, so the discharge of untreated sludge can cause serious pollution to the environment and loss of useful components in the sludge. The selectable sustainable treatment and disposal process mainly comprises sludge land utilization, sludge incineration and building material utilization.
In the aspect of land utilization, although the sludge of domestic sewage plants has low heavy metal content, the salt, pathogens and organic pollutants (including hormones, antibiotics and plasticizers) in the sludge pollute soil, surface water and underground water to cause secondary pollution, and in addition, the market acceptance of the sludge products entering the farmland for utilization is low, and the sludge products are not permitted to enter the farmland for utilization in the clear text of China, so certain environmental risks exist in the land agriculture. The urban landscaping and land improvement are common in China, but the consumption of the urban landscaping and land improvement is limited.
The utilization of the sludge building materials is relatively widespread, such as brick making, cement manufacturing, ceramsite manufacturing and fiber board manufacturing, but the utilization of the sludge building materials is limited by local or industrial landscape and is not stable.
the sludge can be incinerated independently or mixed with garbage, industrial boilers and thermal power plants, and is relatively flexible. Particularly, the amount of the mixed burning with garbage and a thermal power plant is more, and the amount of the single burning is relatively less. The single incineration is not suitable for projects with small sludge scale, the incineration of the sludge is popular with people once, however, the sludge incineration is limited in use by large one-time investment, high equipment investment, high operation cost, generation of dioxin and other highly toxic substances when the combustion temperature of organic matters is lower than 850 ℃, treatment of flue gas, retreatment of incineration ash and the like.
In addition, in the existing domestic and foreign sludge treatment modes, the drying mostly adopts the forms of heat drying and composting, although methods of optimizing heat sources, reducing process steps, optimizing operation parameters and the like are adopted to reduce energy consumption, the process must utilize an external heating source, so that the development of the heat drying process is limited.
Disclosure of Invention
the invention aims to: aiming at the problems in the prior art, the Aeromonas reinhardtii preparation for treating domestic sludge and the preparation method and application thereof are provided, have good removal effect on peculiar smell and water content of the sludge, do not need an external heating source, are environment-friendly, energy-saving, economical and reliable, are convenient to treat, and convert the sludge into a soil conditioner which has high organic value, no peculiar smell and stable properties.
The technical scheme adopted by the invention is as follows:
A preparation method of an aeromonas rillii preparation for treating domestic sludge comprises the following steps:
s1, soaking fresh earthworm cast in water for 30-40min, and taking a soaking solution;
s2, adding the soak solution obtained in the step S1, the Aeromonas reinhardtii strain and the culture medium into a culture container, and culturing at the temperature of 12-15 ℃ for 11-13h to obtain a culture mother solution;
And S3, adding a culture medium into the culture mother liquor obtained in the step S2, and culturing at normal temperature for 11-13h to obtain the culture medium.
The principle of treating the domestic sludge by adopting the method is to simulate the metabolic mode of the earthworms, the aeromonas reesei in the earthworm metabolites is gram negative, the cells of the straightstock with round ends are approximately spherical, and the diameter is 0.3-1.0 mu m. Single, paired or short chain. The bacterial colony is light yellow, has regular edges, smooth surface, facultative anaerobism and chemoheterotrophy. The optimum growth temperature is 30 ℃. The product is positive in oxidase and catalase, and can degrade cellulose substances (sodium carboxymethyl cellulose) into monosaccharide to form a transparent ring on a Congo red culture medium. Cellulose degrading bacteria can degrade cellulose substances (sodium carboxymethyl cellulose) into monosaccharide. The aeromonas reinhardtii has the functions of rapidly metabolizing water in the sludge, breaking the constraint of a flocculating agent and the like, so that the sludge is converted into a soil conditioner which has high organic value, no peculiar smell and stable properties. After the microorganisms are propagated in a large amount under a proper culture method and culture conditions, sufficient ventilation and oxygen supply can be ensured under the condition of a temperature much lower than that of an aerobic composting method and a biological drying method, and sludge with the water content of about 80 percent is converted into a soil conditioner with the water content of less than 60 percent in 10 to 15 days.
The invention mainly comprises two stages for treating domestic sludge: 1) mainly adopts microbial inoculum treatment. The microbial inoculum metabolizes water in the sludge, stabilizes organic matters, breaks the constraint of a flocculating agent and releases bound water. 2) Mainly natural evaporation. After the structure of the binding water of the flocculant of the sludge is broken, the sludge becomes loose and porous, and the water is removed by natural evaporation.
further, the ratio of the wormcast to the water in the step S1 is 0.38-0.50 g: 1 mL.
Further, the culture medium in the steps of S2 and S3 comprises the following components in a mass ratio of 4: 1: 1: 1: 1000 of beef extract, corn flour, peptone, sodium chloride and water.
further, the volume ratio of the culture medium, the soak solution and the aeromonas reinhardtii strain in the step S2 is 5-5.5: 0.1-0.15: 0.01-0.015.
Further, the volume ratio of the culture medium, the soak solution and the aeromonas reiliana strain in the step S2 is 5:0.1: 0.01.
Further, the volume ratio of the culture medium to the culture mother liquor in the step S3 is 10-10.5: 0.2-0.25.
Further, the volume ratio of the medium to the culture mother liquor in the step S3 was 10: 0.2.
The aeromonas rillii preparation for treating the domestic sludge is prepared by the preparation method.
the application of the aeromonas reiliana preparation in treating domestic sludge.
The application specifically includes: uniformly spraying the Aeromonas reinhardtii preparation on the domestic sludge, uniformly turning over, and keeping ventilation in the domestic sludge treatment process for 10-15 days; the volume ratio of the aeromonas reiliana preparation to the domestic sludge is 1: 2.5.
in summary, due to the adoption of the technical scheme, the invention has the beneficial effects that:
1. according to the invention, the culture mode and the operation flow of the aeromonas reesei are simple and easy to operate, the wormcast soak solution is adopted for culture, the raw materials are easy to obtain, and the microorganisms in the wormcast and the aeromonas reesei used in the invention play a synergistic effect in the treatment process of the domestic sludge, break the constraint of a flocculating agent and rapidly metabolize the moisture in the sludge;
2. The Aeromonas reinhardtii preparation prepared by the invention has no secondary pollution when being used for treating the domestic sludge, and the obtained soil has high organic value, no peculiar smell and stable properties, and can be used for gardens, land agriculture and the like;
3. The treatment period is short, only 10-15 days are needed, and the sticky sludge with the water content of about 80% can be converted into the odorless loose soil with the water content of less than 60%;
4. The method of the invention for treating the domestic sludge meets the requirements of national resource sustainable development and has low treatment cost, so that the product has great market advantages.
Detailed Description
in order to make the objects, technical solutions and advantages of the present invention more apparent, the present invention is further described in detail with reference to the following embodiments. It should be understood that the detailed description and specific examples, while indicating the preferred embodiment of the invention, are intended for purposes of illustration only and are not intended to limit the scope of the invention.
Thus, the following detailed description of the embodiments of the present invention is not intended to limit the scope of the invention as claimed, but is merely representative of selected embodiments of the invention. All other embodiments, which can be derived by a person skilled in the art from the embodiments of the present invention without making any creative effort, shall fall within the protection scope of the present invention.
It is noted that relational terms such as "first" and "second," and the like, may be used solely to distinguish one entity or action from another entity or action without necessarily requiring or implying any actual such relationship or order between such entities or actions. Also, the terms "comprises," "comprising," or any other variation thereof, are intended to cover a non-exclusive inclusion, such that a process, method, article, or apparatus that comprises a list of elements does not include only those elements but may include other elements not expressly listed or inherent to such process, method, article, or apparatus. Without further limitation, an element defined by the phrase "comprising an … …" does not exclude the presence of other identical elements in a process, method, article, or apparatus that comprises the element.
The features and properties of the present invention are described in further detail below with reference to examples.
Example 1
The preparation method of the aeromonas reiliana preparation for treating the domestic sludge provided by the preferred embodiment of the invention comprises the following specific steps:
s1, soaking fresh wormcast in water for 30min, taking a soaking solution, wherein the ratio of wormcast to water is 0.38 g: 1 mL;
S2, adding the soaking solution obtained in the step S1, the Aeromonas reinhardtii strain and the culture medium into a culture container according to the volume ratio of the culture medium to the Aeromonas reinhardtii strain of 5:0.1:0.01, and culturing at 12 ℃ for 12 hours to obtain a culture mother solution;
S3, dispersing the culture mother liquor obtained in the step S2 in a culture bucket, adding a culture medium into the culture bucket, wherein the volume ratio of the culture medium to the culture mother liquor is 10:0.2, and culturing at normal temperature for 12 hours to obtain the culture medium.
wherein the culture medium is a commercial culture medium and comprises the following components in a mass ratio of 4: 1: 1: 1: 1000 of beef extract, corn flour, peptone, sodium chloride and water.
Example 2
The preparation method of the aeromonas reiliana preparation for treating the domestic sludge provided by the preferred embodiment of the invention comprises the following specific steps:
s1, soaking fresh wormcast in water for 30min, taking a soaking solution, wherein the ratio of wormcast to water is 0.50 g: 1 mL;
S2, adding the soaking solution obtained in the step S1, the Aeromonas reinhardtii strain and the culture medium into a culture container according to the volume ratio of the culture medium to the Aeromonas reinhardtii strain of 5.2:0.1:0.01, and culturing at 13 ℃ for 12 hours to obtain a culture mother solution;
S3, dispersing the culture mother liquor obtained in the step S2 in a culture bucket, adding a culture medium into the culture bucket, wherein the volume ratio of the culture medium to the culture mother liquor is 10.2:0.2, and culturing at normal temperature for 12 hours to obtain the culture medium.
Wherein the culture medium is a commercial culture medium and comprises the following components in a mass ratio of 4: 1: 1: 1: 1000 of beef extract, corn flour, peptone, sodium chloride and water.
example 3
The preparation method of the aeromonas reiliana preparation for treating the domestic sludge provided by the preferred embodiment of the invention comprises the following specific steps:
S1, soaking fresh wormcast in water for 30min, taking a soaking solution, wherein the ratio of wormcast to water is 0.45 g: 1 mL;
S2, adding the soaking solution obtained in the step S1, the Aeromonas reinhardtii strain and the culture medium into a culture container according to the volume ratio of the culture medium to the Aeromonas reinhardtii strain of 5.5:0.1:0.01, and culturing at 15 ℃ for 12 hours to obtain a culture mother solution;
S3, dispersing the culture mother liquor obtained in the step S2 in a culture bucket, adding a culture medium into the culture bucket, wherein the volume ratio of the culture medium to the culture mother liquor is 10.5:0.2, and culturing at normal temperature for 12 hours to obtain the culture medium.
Wherein the culture medium is a commercial culture medium and comprises the following components in a mass ratio of 4: 1: 1: 1: 1000 of beef extract, corn flour, peptone, sodium chloride and water.
Example 4
The preparation method of the aeromonas reiliana preparation for treating the domestic sludge provided by the preferred embodiment of the invention comprises the following specific steps:
S1, soaking fresh wormcast in water for 30min, taking a soaking solution, wherein the ratio of wormcast to water is 0.42 g: 1 mL;
S2, adding the soaking solution obtained in the step S1, the Aeromonas reinhardtii strain and the culture medium into a culture container according to the volume ratio of the culture medium to the Aeromonas reinhardtii strain of 5.3:0.1:0.01, and culturing at 14 ℃ for 12 hours to obtain a culture mother solution;
S3, dispersing the culture mother liquor obtained in the step S2 in a culture bucket, adding a culture medium into the culture bucket, wherein the volume ratio of the culture medium to the culture mother liquor is 10.3:0.2, and culturing at normal temperature for 12 hours to obtain the culture medium.
wherein the culture medium is a commercial culture medium and comprises the following components in a mass ratio of 4: 1: 1: 1: 1000 of beef extract, corn flour, peptone, sodium chloride and water.
Example 5
the preparation method of the aeromonas reiliana preparation for treating the domestic sludge provided by the preferred embodiment of the invention comprises the following specific steps:
S1, soaking fresh wormcast in water for 30min, taking a soaking solution, wherein the ratio of wormcast to water is 0.48 g: 1 mL;
S2, adding the soaking solution obtained in the step S1, the Aeromonas reinhardtii strain and the culture medium into a culture container according to the volume ratio of the culture medium to the Aeromonas reinhardtii strain of 5:0.12:0.01, and culturing at 12 ℃ for 12 hours to obtain a culture mother solution;
S3, dispersing the culture mother liquor obtained in the step S2 in a culture bucket, adding a culture medium into the culture bucket, wherein the volume ratio of the culture medium to the culture mother liquor is 10:0.21, and culturing at normal temperature for 12 hours to obtain the culture medium.
Wherein the culture medium is a commercial culture medium and comprises the following components in a mass ratio of 4: 1: 1: 1: 1000 of beef extract, corn flour, peptone, sodium chloride and water.
example 6
the preparation method of the aeromonas reiliana preparation for treating the domestic sludge provided by the preferred embodiment of the invention comprises the following specific steps:
S1, soaking fresh wormcast in water for 30min, taking a soaking solution, wherein the ratio of wormcast to water is 0.40 g: 1 mL;
s2, adding the soaking solution obtained in the step S1, the Aeromonas reinhardtii strain and the culture medium into a culture container according to the volume ratio of the culture medium to the Aeromonas reinhardtii strain of 5.1:0.13:0.01, and culturing at 13 ℃ for 12 hours to obtain a culture mother solution;
S3, dispersing the culture mother liquor obtained in the step S2 in a culture bucket, adding a culture medium into the culture bucket, wherein the volume ratio of the culture medium to the culture mother liquor is 10.2:0.23, and culturing at normal temperature for 12 hours to obtain the culture medium.
Wherein the culture medium is a commercial culture medium and comprises the following components in a mass ratio of 4: 1: 1: 1: 1000 of beef extract, corn flour, peptone, sodium chloride and water.
Examples of the experiments
the Aeromonas reinhardtii preparation prepared in example 1 was used to treat domestic sludge, and various index parameters before and after the treatment of the domestic sludge were measured.
The processing method comprises the following steps: uniformly spraying the Aeromonas reinhardtii preparation on domestic sludge and uniformly turning over, wherein the volume ratio of the Aeromonas reinhardtii preparation to the domestic sludge is 1: 2.5, keeping ventilation in the domestic sludge treatment process, and treating for 12 d.
TABLE 1 index parameters before and after treatment of domestic sludge
| water content (%) | Smell(s) | Form of the composition | |
| before treatment | 80 | Strong ammonia and hydrogen sulfide odor | grey black, viscous jelly-like |
| After treatment | ＜60 | Has no peculiar smell | Yellow, loose and loose |
As can be seen from the above Table 1, the domestic sludge treated by the preparation and the method of the present invention has great differences in moisture content, appearance and odor from the domestic sludge before treatment, and has no peculiar smell, loose form and low moisture content, which indicates that the preparation of the present invention has good effect in treating the domestic sludge.
Comparative example
the domestic sludge was treated by 4 different methods, i.e., by using the Aeromonas reinhardtii preparation prepared in example 1 of the present invention, incineration, composting and biological drying, and the results are shown in Table 2 below:
Table 2 comparative experiments and related data
The above description is only for the purpose of illustrating the preferred embodiments of the present invention and is not to be construed as limiting the invention, and any modifications, equivalents and improvements made within the spirit and principle of the present invention are intended to be included within the scope of the present invention.
Claims (10)
1. a preparation method of an aeromonas rillii preparation for treating domestic sludge is characterized by comprising the following steps:
s1, soaking fresh earthworm cast in water for 30-40min, and taking a soaking solution;
S2, adding the soak solution obtained in the step S1, the Aeromonas reinhardtii strain and the culture medium into a culture container, and culturing at the temperature of 12-15 ℃ for 11-13h to obtain a culture mother solution;
And S3, adding a culture medium into the culture mother liquor obtained in the step S2, and culturing at normal temperature for 11-13h to obtain the culture medium.
2. The method for preparing an aeromonas reishi preparation for treating domestic sludge according to claim 1, wherein the method comprises the steps of: the ratio of the wormcast to the water in the step S1 is 0.38-0.50 g: 1 mL.
3. The method for preparing an aeromonas reishi preparation for treating domestic sludge according to claim 1, wherein the method comprises the steps of: the culture medium in the S2 and S3 steps comprises the following components in a mass ratio of 4: 1: 1: 1: 1000 of beef extract, corn flour, peptone, sodium chloride and water.
4. The method for producing an aeromonas reishi preparation for treating domestic sludge according to claim 3, wherein: the volume ratio of the culture medium, the soak solution and the Aeromonas reinhardtii strain in the step S2 is 5-5.5: 0.1-0.15: 0.01-0.015.
5. The method for producing an aeromonas reishi preparation for treating domestic sludge according to claim 4, wherein the method comprises the steps of: the volume ratio of the culture medium, the soak solution and the Aeromonas reinhardtii strain in the step S2 is 5:0.1: 0.01.
6. the method for producing an aeromonas reishi preparation for treating domestic sludge according to claim 3, wherein: the volume ratio of the culture medium to the culture mother liquor in the step S3 is 10-10.5: 0.2-0.25.
7. The method for producing an aeromonas reishi preparation for treating domestic sludge according to claim 6, wherein the method comprises the steps of: the volume ratio of the culture medium to the culture mother liquor in the step S3 is 10: 0.2.
8. An aeromonas reesei preparation for treating domestic sludge prepared by the preparation method according to any one of claims 1 to 7.
9. use of the Aeromonas reesei formulation of claim 8 in the treatment of domestic sludge.
10. the use according to claim 9, characterized in that it is in particular: uniformly spraying the Aeromonas reinhardtii preparation on the domestic sludge, uniformly turning over, and keeping ventilation in the domestic sludge treatment process for 10-15 days; wherein the volume ratio of the aeromonas rillii preparation to the domestic sludge is 1: 2.5.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201910928200.6A CN110551663A (en) | 2019-09-28 | 2019-09-28 | Aeromonas rillii preparation for treating domestic sludge and preparation method and application thereof |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201910928200.6A CN110551663A (en) | 2019-09-28 | 2019-09-28 | Aeromonas rillii preparation for treating domestic sludge and preparation method and application thereof |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN110551663A true CN110551663A (en) | 2019-12-10 |
Family
ID=68741788
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201910928200.6A Withdrawn CN110551663A (en) | 2019-09-28 | 2019-09-28 | Aeromonas rillii preparation for treating domestic sludge and preparation method and application thereof |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN110551663A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN112857921A (en) * | 2021-03-04 | 2021-05-28 | 天津科技大学 | Method for evaluating odor reduction effect of microbial agent pretreatment on dried sludge finished product in two-stage method |
Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS51133954A (en) * | 1975-05-14 | 1976-11-20 | Kuraray Co Ltd | Sewage disposal method |
| JP2003062599A (en) * | 2001-06-14 | 2003-03-04 | Nkk Corp | Method for treating sludge utilizing microorganism |
| CN102515450A (en) * | 2011-10-22 | 2012-06-27 | 徐瑞金 | Municipal sewage sludge treatment method and its product |
| CN102776138A (en) * | 2012-05-02 | 2012-11-14 | 山西大同大学 | Compound microorganism preparation for materialized sludge treatment and method for preparing same |
| CN104087536A (en) * | 2014-07-10 | 2014-10-08 | 安徽农业大学 | Household sludge reduction compound microbial preparation as well as preparation and application methods thereof |
| CN109161503A (en) * | 2018-09-18 | 2019-01-08 | 陕西文岭微生物科技有限公司 | For handling the composite bacteria agent of sludge and the technique of preparation method and processing sludge |
-
2019
- 2019-09-28 CN CN201910928200.6A patent/CN110551663A/en not_active Withdrawn
Patent Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS51133954A (en) * | 1975-05-14 | 1976-11-20 | Kuraray Co Ltd | Sewage disposal method |
| JP2003062599A (en) * | 2001-06-14 | 2003-03-04 | Nkk Corp | Method for treating sludge utilizing microorganism |
| CN102515450A (en) * | 2011-10-22 | 2012-06-27 | 徐瑞金 | Municipal sewage sludge treatment method and its product |
| CN102776138A (en) * | 2012-05-02 | 2012-11-14 | 山西大同大学 | Compound microorganism preparation for materialized sludge treatment and method for preparing same |
| CN104087536A (en) * | 2014-07-10 | 2014-10-08 | 安徽农业大学 | Household sludge reduction compound microbial preparation as well as preparation and application methods thereof |
| CN109161503A (en) * | 2018-09-18 | 2019-01-08 | 陕西文岭微生物科技有限公司 | For handling the composite bacteria agent of sludge and the technique of preparation method and processing sludge |
Non-Patent Citations (2)
| Title |
|---|
| 林春骏等: "污水处理厂接种物的多样性及对化学品生物降解的影响 ", 《生态与农村环境学报》 * |
| 石春芳等: "微生物絮凝剂产生菌的分离选育及鉴定 ", 《包头钢铁学院学报》 * |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN112857921A (en) * | 2021-03-04 | 2021-05-28 | 天津科技大学 | Method for evaluating odor reduction effect of microbial agent pretreatment on dried sludge finished product in two-stage method |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN101746941B (en) | Biological drying method for treating dewatered sludge of urban sewage plant | |
| CN101787350B (en) | Functional composite biological agent for high-efficiency degradation of household refuses and application thereof | |
| CN111500495B (en) | A kind of composite microbial deodorant and preparation method thereof | |
| CN104449744A (en) | Microbial soil remediation agent and preparation method thereof | |
| CN103497905B (en) | A kind of efficient denitrification flcos producing bacteria strain and application thereof | |
| CN108165509A (en) | Compound micro-ecological preparation for the black smelly water harnessing in river and preparation method thereof | |
| CN106282061A (en) | For complex microorganism preparations that black-odor riverway is administered and its preparation method and application | |
| CN106701628B (en) | Rural domestic garbage fermentation microbial inoculum and use method and application thereof | |
| CN105296398A (en) | Low-temperature-resistant composite microbial agent used for treating contaminated water, and preparation method and application thereof | |
| CN102408259B (en) | Solid waste co-composting stepwise regulation and control system and method | |
| CN114214227A (en) | Microbial agent for municipal sludge drying treatment and preparation method thereof | |
| CN106865750A (en) | A kind of activated sludge culture and acclimation method for difficult for biological degradation organic wastewater biological treatment | |
| CN100484895C (en) | Method for treating sludge by earthwork stacking | |
| CN105316312A (en) | Breeding method for increasing paenibacillus sugar yield and application thereof | |
| CN112375721A (en) | Preparation method and application of composite microbial inoculum for low-temperature treatment of rural domestic sewage | |
| CN110551663A (en) | Aeromonas rillii preparation for treating domestic sludge and preparation method and application thereof | |
| CN101307234B (en) | A kind of low-yield field soil organic amendment and preparation method thereof | |
| CN110591959A (en) | Proteus mirabilis preparation for treating domestic sludge and preparation method and application thereof | |
| 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 | |
| CN106927635A (en) | Energy output type sewage treatment process | |
| CN115353211A (en) | Application of bacillus megaterium LZP03 in treatment of pig raising wastewater | |
| Chen | Sewage sludge aerobic composting technology research progress | |
| CN104212748A (en) | Denitrifying phosphorus accumulation bacterial strain and method for removing nitrate nitrogen and total phosphorus in wastewater by utilizing denitrifying phosphorus accumulation bacterial strain | |
| CN110591958A (en) | Morganella morganii preparation for treating domestic sludge and preparation method and application thereof | |
| CN112723941A (en) | Nitrogen and phosphorus preservation composting method for municipal domestic sludge |
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 | ||
| WW01 | Invention patent application withdrawn after publication |
Application publication date: 20191210 |