CN1057673A - Preservation process of activated sludge - Google Patents
Preservation process of activated sludge Download PDFInfo
- Publication number
- CN1057673A CN1057673A CN 90104329 CN90104329A CN1057673A CN 1057673 A CN1057673 A CN 1057673A CN 90104329 CN90104329 CN 90104329 CN 90104329 A CN90104329 A CN 90104329A CN 1057673 A CN1057673 A CN 1057673A
- Authority
- CN
- China
- Prior art keywords
- active sludge
- activated sludge
- sludge
- preservation process
- preservation
- 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
Links
Landscapes
- Treatment Of Sludge (AREA)
Abstract
Preservation process of activated sludge, a kind of microbial preservation technique can be preserved active sludge in large quantities, chronically.The present invention carries out decontamination to active sludge, and dosing mixes, and technological methods such as can are placed in the pond or in the air and preserve after handling, and reserve capacity generally can reach 1.2M
3, also can preserve the active sludge of specific quantity according to actual needs.
Description
Preservation process of activated sludge, a kind of microbial preservation technique.
At present, in scientific experiment such as biotechnology with microorganism is had in the industrial production of particular requirement, microorganism is required not pollute, do not make a variation; To the preservation of active sludge, regular transplanting culture method is arranged, continuous culture method, lyophilize preservation method, distilled water suspension preservation method, and technological method such as buffered soln suspension preservation method.The method that adopts in the practical application generally all needs specific installation, preserves container and adopts test tube, and reserve capacity is less.Also there is reserve capacity bigger, as beer production dull season, when brew-house does not have sewage disposal, just need to preserve active sludge to produce needs after guaranteeing, what its preservation method adopted is continuous culture method, promptly constantly add nutriment, the same aeration that carries out is handled during with production run, makes human and material resources, financial resources consumption bigger like this.The present invention is improved existing buffered soln preservation method, adopts porous medium absorption stabilization method, and after active sludge carried out pre-treatment, makes active sludge obtain for a long time, preserve in large quantities.
Purpose of the present invention is to create and a kind ofly preserves active sludge in large quantities, chronically and other has a kind of industrial application technological method of preserving the bacterial classification that requires.
Technical process of the present invention is as follows: earlier the impurity of microorganism absorption in the active sludge is removed; Preparation contains the solution of following material then,
CaCl
220-410 mg/L,
NaCl 50-20000 mg/L,
K
2HPO
40-920 mg/L,
KH
2PO
40-720 mg/L,
Na
2HPO
40-760 mg/L,
MgSO
450-241.5 mg/L;
Then will remove the mud of impurity and add in the salts solution for preparing, making sludge concentration is 2%-6%, and fully stirs; At last saliferous mud is poured in the porous support material of sponge kind into, be placed in container or the air.The sludge carrier of this sponge kind porous mass, its aperture requires at 0.1-2mm, and is connected between the Kong Yukong, and between preservation period, porous mass hole planted agent is full of water medium.
The present invention preserves active sludge, and maximum duration can reach more than 1 year; Use method of the present invention not need Special Equipment, method is simple and practical, and is manually actuated; The present invention is strong to environmental adaptability; Can place the container of moisture medium during preservation, also can place air, preserving type is decided on shelf time length; The porous carrier materials that the present invention uses is easy to get, and volume can be cut apart change, takes mud conveniently, can preserve active sludge in a large number, and necessary expense is lower.
Description of drawings of the present invention: this is a process flow sheet of the present invention, and the first step is the impurity of removing in the active sludge; Second step was the saline solns that mud is preserved in preparation; The 3rd step was saline solution that will prepare and the mud of cleaning, and be mixed in proportion, and fully stirring made evenly; The 4th step was that the saliferous mud that mixes is irritated in the porous material carrier, placed the container or the air of water medium.
Embodiment: from handling the active sludge 1m after sedimentation is got in the field
3, add low chlorine tap water or distilled water 1m
3Fully agitator treating leaches washing water through sedimentation then, and repetitive scrubbing (general 4 times) reaches below the 5mg/L up to the washing water BOD that leaches and gets final product, and afterwards, mud 1m was got in sedimentation in 1 hour
3Stand-by, note not getting the impurity that is deposited in the mud sump bottom when getting mud; In addition, at 0.1m
3Low chlorine water in add NaCl 21.6kg, K
2HPO
40.138kg, KH
2PO
40.108kg, Na
2HPO
40.114kg, MgSO
40.096kg, CaCl
2, 0.24kg stirs it is dissolved fully; Above mixed salts solution is added to cleans the back and take out in the stand-by active sludge, and stir to make and mix, mix and add an amount of water in the process again and make the saliferous sludge concentration reach 4.5%; At last, the saliferous mud with 4.5% is poured in the cavernous body that the aperture is 1mm, is placed in the pond of low chlorine water to preserve, and reserve capacity is 1.2M
3
Claims (1)
1, preservation process of activated sludge, particularly a kind of by decontamination, dosing mixes, and the preservation process of activated sludge that technological methods such as can are formed is characterized in that:
One, the active sludge that need are preserved must wash decontamination, removes the impurity of mud sump bottom when taking;
When two, preparing saline solns, add Mg salt, Ca salt as conditioning agent;
Three, the saliferous mud can after the mixing and stirring is preserved in cavernous body class porous mass carrier.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 90104329 CN1057673A (en) | 1990-06-23 | 1990-06-23 | Preservation process of activated sludge |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 90104329 CN1057673A (en) | 1990-06-23 | 1990-06-23 | Preservation process of activated sludge |
Publications (1)
Publication Number | Publication Date |
---|---|
CN1057673A true CN1057673A (en) | 1992-01-08 |
Family
ID=4878513
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN 90104329 Pending CN1057673A (en) | 1990-06-23 | 1990-06-23 | Preservation process of activated sludge |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN1057673A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1295162C (en) * | 2005-01-19 | 2007-01-17 | 南京大学 | Method for enhancing activity of anaerobic sludge by using rare earth |
CN100350037C (en) * | 2006-03-30 | 2007-11-21 | 山东大学 | Prodn. process of dry aerobic granulated sludge specially for degrading toxic organics |
CN101264977B (en) * | 2008-04-28 | 2010-10-13 | 哈尔滨工业大学 | Device and method for conserving anaerobic particle sludge in beer industrial waste water treatment |
-
1990
- 1990-06-23 CN CN 90104329 patent/CN1057673A/en active Pending
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1295162C (en) * | 2005-01-19 | 2007-01-17 | 南京大学 | Method for enhancing activity of anaerobic sludge by using rare earth |
CN100350037C (en) * | 2006-03-30 | 2007-11-21 | 山东大学 | Prodn. process of dry aerobic granulated sludge specially for degrading toxic organics |
CN101264977B (en) * | 2008-04-28 | 2010-10-13 | 哈尔滨工业大学 | Device and method for conserving anaerobic particle sludge in beer industrial waste water treatment |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
US5840182A (en) | Apparatus and method for biological purification of waste | |
CN109609406A (en) | A kind of slow-release microbial bacterial agent and preparation method thereof administered for black and odorous water | |
JPS6339692A (en) | Preventing method and treating materials for putrefaction of water and generation of slime and algae in circulating system and non-circulating system | |
US4529701A (en) | Product and process for stimulating bacterial action in an anaerobic digestion system | |
JPH1085782A (en) | Bacterium implantation tool | |
CN101798137B (en) | Method for preparing novel hydrophilic and magnetic mesh organism | |
JPH1142496A (en) | Method and device for purifying contaminated waste water by microorganism | |
CN1057673A (en) | Preservation process of activated sludge | |
JPH09187792A (en) | Drainage treatment method and usable bacteria activating tank | |
CN216711837U (en) | Novel biological filter sewage deodorization device | |
JPS61118189A (en) | Method for accelerating action of microbe | |
JP2000342670A (en) | Deodorizing agent, deodorizing method, deodorizing member, and deodorizing device | |
JP3385074B2 (en) | Microbial treatment of wastewater containing oils and fats | |
JPH0760276A (en) | Preserved bacterium for waste water treatment, and waste water treatment method with preserved bacterium | |
CN209507740U (en) | Integrated sewage disposal equipment for reclaiming | |
CN202823167U (en) | Deodorization member and deodorization device | |
WO1998013307A1 (en) | Immobilised porous ceramic (ipc) material for the biological purification of wastewater or natural water contaminated by xenobiotics | |
JPS6029559B2 (en) | wastewater treatment equipment | |
CN107140795B (en) | Environment-friendly process for treating domestic wastewater of power plant | |
CN107089775A (en) | Container-type variable volume integrated effluent disposal system | |
Pajak et al. | Treatment of poultry manure wastewater using a rotating biological contactor | |
JPH0137986B2 (en) | ||
JPH04505279A (en) | Wastewater treatment | |
KR960041138A (en) | Method of manufacturing plant nutrients | |
JPS60225694A (en) | Treatment of waste water |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C01 | Deemed withdrawal of patent application (patent law 1993) | ||
WD01 | Invention patent application deemed withdrawn after publication |