CN101962255A - Method for effective sterilization and efficient hydration of primary sludge - Google Patents

Method for effective sterilization and efficient hydration of primary sludge Download PDF

Info

Publication number
CN101962255A
CN101962255A CN 201010280095 CN201010280095A CN101962255A CN 101962255 A CN101962255 A CN 101962255A CN 201010280095 CN201010280095 CN 201010280095 CN 201010280095 A CN201010280095 A CN 201010280095A CN 101962255 A CN101962255 A CN 101962255A
Authority
CN
China
Prior art keywords
primary sludge
sludge
water
slurries
slurry
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.)
Granted
Application number
CN 201010280095
Other languages
Chinese (zh)
Other versions
CN101962255B (en
Inventor
梁杞香
唐建新
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.)
Hunan Huaqing Thai Sludge Treatment Technology Co. Ltd.
Original Assignee
CHANGSHA JIEXIANG ENVIRONMENTAL ENGINEERING 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 CHANGSHA JIEXIANG ENVIRONMENTAL ENGINEERING Co Ltd filed Critical CHANGSHA JIEXIANG ENVIRONMENTAL ENGINEERING Co Ltd
Priority to CN2010102800959A priority Critical patent/CN101962255B/en
Publication of CN101962255A publication Critical patent/CN101962255A/en
Application granted granted Critical
Publication of CN101962255B publication Critical patent/CN101962255B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Treatment Of Sludge (AREA)

Abstract

The invention discloses a method for effective sterilization and efficient hydration of primary sludge, which comprises the following steps of: (1) primary sludge acidifying treatment for preparing slurry; (2) microwave heating sterilization: heating the slurry to between 30 and 90 DEG C; (3) mechanical filtration: performing solid-liquid separation on the microwave heated slurry, and washing the solid by using water to obtain dry sludge residue and new slurry; and (4) adjusting pH value of the new slurry to be between 6.0 and 8.5 by using lime, wherein the new slurry can be used as circulating water for sludge acidification for preparing the slurry and separation and washing of the mechanical filtration, and the rest recycled partial new slurry can be returned to a sewage treatment system of a sewage treatment plant. The method realizes direct effective sterilization and efficient hydration of the primary sludge generated by the sewage treatment plant without the processes of secondary deposition, concentration, digestion and the like, and can save a large amount of operating cost.

Description

The method of effective sterilization of a kind of primary sludge and high-efficiency dehydration
Technical field
The present invention relates to the primary sludge dehydration of sewage work and the method for effective germicidal treatment, be specially the method for effective sterilization of a kind of primary sludge and high-efficiency dehydration.
Background technology
At present, in the ever-increasing while of wastewater treatment in China ability, town sewage is handled the mud that produces and is also constantly increased.Original most mud own do not obtain appropriate disposal, the phenomenon of arbitrarily abandoning, toppling over is ubiquity also, the secondary pollution problem that causes thus can not be ignored, to a certain extent even offset the achievement of pollution emission reduction, some areas are also improper because of sludge disposal, caused the environmental pollution incident.
Mud is the solidliquid mixture that is produced in each unit of Sewage treatment systems, is the accessory products of sewage treatment process, and its fundamental characteristics is as follows:
1) mud contains the hazardous and noxious substances of a large amount of organic matters, pathogenic agent, parasite and difficult degradation except that containing ash content.In treating processes, be difficult to bacterium is thoroughly eliminated.Mud is to be main microorganism and suspended matter, colloidalmaterial formed umbrinaceous flocs unit mixed in together by bacterium, microfauna.Microorganism wherein mainly is made up of bacterium, bacterium mainly contains zoogloea bacterium and thread fungus, quantity can account for about 90%~95% of microorganism total amount in the mud, bacterium plays most important effect in the processing of organic waste water, as in follow-up A-B activated sludge process, the A section is moved under very high load, the residence time, mud are all shorter relatively the length of time, in this case, higher eukaryotic microorganisms can't be survived, and the protokaryon bacterium that has only some to lack the generation could adapt to, survive and be able to growth and breeding.In addition, also have microfaunas such as protozoon and metazoan in the active sludge.Handling life SewageActive sludge in have a large amount of protozoons and the miniature metazoan of part, assert its kind by distinguishing, therefore quality that in view of the above can juggling water quality is called microfauna the indicator organism in the Sludge System.
2) moisture percentage in sewage sludge height, the primary sludge water ratio reaches 97~99.5%, still moisturely after the concentration reaches 80~85%, and volume is bigger, transportation inconvenience, landfill inconvenience brings serious secondary pollution and potentially contaminated.
3) compound that contains of mud itself produces gas and forms the foreign odor flavor, under action of microorganisms, produces a large amount of stenches especially, is difficult to remove.This problem has all been avoided in general sludge treatment base.
In the mud of dirty (giving up) water treatment, particle is thinner, and density is less, the high and difficult water of removing of water ratio; Organic soil ulmin (preliminary sedimentation tank mud contains 33%, and digested sludge contains 35%, and active sludge contains 41%, and rotten mud contains 47%) content height is degenerated smellyly easily, has built the good environment of existence and breeding for various a large amount of pathogenic bacteria, parasite, microorganisms; Owing to be mixed with hospital's draining and some trade effluent in the municipal effluent, usually contain a large amount of hazardous and noxious substances such as heavy metal in the mud, and these materials be wrapped in by microorganism, bacterium again, thereby be difficult to remove.Can cause bigger harm to environment and the mankind and animal health, the eubiosis.
If mud can not carry out harmlessness disposing, under certain conditions, this transformation even may make some noxious pollutant (as the microorganism that contains heavy metal ion, carries the germs of a disease) enrichment, and cause serious secondary pollution and potential pollution in modes such as carriers such as water, air, mosquitos and flies muroid animal, biochemical decompositions of solid permeate, spread, dissociate because it contains poisonous objectionable constituent; It is relevant to cause the reason of this situation and existing sludge treatment disposal technology in the world to be not suitable for China's national situation, also because sanitary sewage and trade effluent merge handles, thereby makes the composition of mud very complicated, is difficult to handle.
The notable attribute of mud is the water ratio height, and is therefore bulky, its major cause be exactly main component in the mud be to be that carrier exists with the bacterium, the interstitial water of bacterium generally will account for 65%~85% of total water content in the mud; Next be capillary water account for total water content in the mud 15%~25%.Because the bonding force between capillary water and the mud granule is stronger, inspissated can not with the capillary combined moisture from, need by higher mechanicals efforts and energy, as vacuum filtration, filtering under pressure and centrifugation could be removed this part moisture will remove this part moisture, must destroy cytolemma, enchylema is oozed out, become outside liquid by the internal junction Heshui.By conventional concentrate, digestion, mechanical filter is difficult to remove, the general still moisture 60-85% of mud after dehydration.
This long distance transhipment and subsequent disposal disposal for mud has brought economically, on the environment, on the safety and technical great difficulty.At present, the treatment technology of domestic sludge dewatering and method mainly contain mud just heavy (two is heavy), concentrate, technologies such as digestion, mechanical dehydration, physics mummification.And by the practical application discovery, these technology investments are big, take up an area of greatly, and energy consumption is big, and the running cost height needs to add multiple a large amount of flocculations (coagulation) agent and processing brings difficulty to subsequent technique, still exists the difficulty of dewatering very big.Under existing technical qualification, generally be to carry out germicidal treatment in the active sludge that in digestive process, produces, do not carry out sterilization in the starting stage (primary sludge).
Mud purposes after dehydration is extensively sent out, and can be used for composting, feed, building materials, fuel etc.Therefore, research and development utilize the novel method of effective sterilization of a kind of primary sludge and high-efficiency dehydration, for innoxious, the minimizing and the follow-up recycling treatment thereof of mud is very necessary.
Summary of the invention
Technical problem solved by the invention is to provide the method for effective sterilization of a kind of primary sludge and high-efficiency dehydration, to solve the problem in the background technology:
Technical problem solved by the invention realizes by the following technical solutions:
The method of effective sterilization of a kind of primary sludge and high-efficiency dehydration may further comprise the steps:
(1) primary sludge acidification: the primary sludge of getting urban wastewater treatment firm, water ratio 97%~99.5%, add entry in the mass ratio of water and primary sludge in 0.2: 1~1: 1 ratio, the mass ratio that in mass concentration is 93%~98% technical grade sulfuric acid and primary sludge adds technical grade sulfuric acid in 0.02: 0.1~0.1: 1 ratio, after stirring 5~10min, add the technical grade hydrogen peroxide in the mass ratio of concentration 27.5%~35% technical grade hydrogen peroxide and primary sludge in 0.02: 0.1~0.1: 1 ratio, stirring reaction 5~10min makes slurries;
(2) microwave pasteurization: slurries are heated to 30 ℃~90 ℃, heat-up time 15~90min;
(3) mechanical filter: the slurries after the microwave heating treatment are carried out solid-liquid separation and wash with water, dewatered sludge slag and new slurries, the mass ratio of washing water consumption and primary sludge 0.3: 1~1: 1;
(4) new slurries are regulated pH value to 6.0~8.5 with lime, and new slurries can be used as the cycling use of water reuse to mud acidifying slurrying liquid and mechanical filter separating, washing, the Sewage treatment systems that the remaining new slurries of part can be sent sewage work back to after the reuse.
The microwave pasteurization principle;
Have many studies show that biological with medical field, microwave heating is different with traditional heating, it does not need thermal conduction from outward appearance to inner essence, but the temperature field and the electromagnetic field that produce by microwave, can be directly and effectively at the inner heat that produces of whole material, promote the molecule high-speed motion of bacterium, difference according to material properties (specific conductivity, magnetic permeability, specific inductivity), heating comes the direct heating material in the waste of energy of material inside, and microwave heating is quickened the extruding of its cytolemma and break to reach germ-resistant purpose.The mud molecule that contains large quantity of moisture is that microorganism and cell thereof are separated out moisture by " moment pulverizing ".
The electromagnetic field that microwave produces is the lethal principal element of bacterium, particularly when lesser temps.A kind of enlightenment of people is given in experiment, the electromagnetic field that makes full use of variation will obtain a kind of newly, germ-resistant means and technology at a lower temperature, start effective sterilization approach." non-hot factor becomes the lethal essential factor of bacterium " that electromagnetic field shows in sterilization process broken the general layout of conventional heat-sterilization, and the bacterium desire is survived and needed the object of fight to change " electromagnetic force " into.The sterilization mechanism of pulse electromagnetic mainly shows following two aspects: electric field action: main biological studies show that of molecule, biological intravital most of molecules and atom have polarity (equivalent electric dipole) and magnetic (molecular current model), so add electromagnetic field and will inevitably exert an influence or act on biology.Add outside under the effect of electromagnetic field, electric dipole and molecular current can be along with the direction orientations of electromagnetic field.In the electromagnetostatic field, just set up a new terminal state; But the time power transformation magnetic field in, electric dipole and molecular current can vibrate along with the variation of electromagnetic field.Obviously, the electromagnetic field that adds that varying strength distributes is different to different biological influence degrees.Medical circle finds that under study for action cell paste has unusual performance in electromagnetic field, and typical performance is to the electromagnetic phenomenon of replying.This biological response phenomenon occurs in away from equilibrium state, and organism is non-linear to the influence of the electromagnetic field that satisfies certain condition, and shows specific frequency function and power specificity.The energy of effect is sometimes from biosystem inside, and external electromagnetic field just plays trigger action.Cell is the most basic bion, and in cell, cytolemma is the part of studying at most.Certain potential difference is all arranged inside and outside each cytolemma, under the effect of extra electric field, the inside and outside potential difference of film can increase, permeability can increase, and cell permeates, and continues appropriateness and handles, when electromagnetic field reaches certain value (E>EO, during H>HO), what cytolemma just took place to repair breaks, and this phenomenon is called electroporation.Simultaneously, because electromagnetic field changes, in the extremely short time, great variation all can take place in the frequency of electromagnetic field, intensity, produces oscillation effect on cytolemma.Irreversible electroporation and fierce oscillation effect can make cell rupture, and this breaking causes the cellularstructure disorder, thereby reaches the purpose of cell killing, and then killing bacteria.Ionizing event: the dielectric barrier that changes electromagnetic field is inhibited to the microorganism of food.Add outside under the effect of electromagnetic field, the charged particle in the mud space will produce high-speed motion, and bump mud molecule makes the mud molecular breakdown, produces the yin, yang ion, and simultaneously, the ionogen electrolysis goes out the yin, yang ion.These yin, yang ions are very active under the effect of strong-electromagnetic field, pass the original cytolemma that has just improved permeability, with living matter in the microorganism such as protein, RNA effect, thereby blocked in the cell normal biochemical and reacted and metabolic carrying out.In addition, electromagnetic field can make the hydrogen-oxygen bond rupture of water molecules, generates excessive ultra-oxygen anion free radical, hydrogen peroxide and free proton in water.And hydrogen peroxide has the intensive oxygenizement, acts on biomolecules, can destroy DNA, causes necrocytosis.The ozone that ionizing event produces in the liquid medium has the intensive oxygenizement equally, can with intracellular matter generation series reaction.More than two kinds of effects unite the principal element that has constituted the killing bacteria body.
Beneficial effect
1, the present invention has realized primary sludge that sewage work is produced directly carrying out effective sterilization and high-efficiency dehydration, no longer through two heavy, concentrate, technology such as digestion, can save great amount of investment, land used and running cost thereof.
2, after the present invention takes acidification, realized changing the purpose of bacteria live environment, for final microwave hyperthermia sterilization provides condition.
3, the present invention takes microwave heating, has realized cold sterilization, sterilization uniform and complete, and the time is short, and the purpose that efficient is high has realized that selectivity adds thermal material, keeps the constant purpose of material component.
4, the primary sludge handled of the present invention can high-efficiency dehydration, drops to 10%~20% by its former water ratio 97%~99.5%, simultaneously the precondition that facilitates for the following process of mud and commercialization.
5 the present invention can adopt the conventional equipment facility of Chemical Manufacture, and one-time investment is few, and the construction period is short, and production cost is low, and Working environment is good, and the operation number is few, grasp operation easily.
Embodiment
The invention will be further described below in conjunction with embodiment.
Embodiment 1 primary sludge sample is taken from husky certain sewage work of Hunan star, and water ratio is 97.5%, and solid content is 2.5%.Evaluation is taken in June, 2010 with sample, the sampling treatment stage of five of extended aeration, the aeration tank mixed solution of active sludge, the excess sludges of the initial stage of primary sludge, active sludge aeration, underload Sludge System respectively, by the full-automatic fast microbiological assessing instrument of MicroStation, identify that initially the microorganism working method is isolated purebred at first routinely.Authentication step is as follows:
1, dull and stereotyped enlarged culturing: use the BIOLOG special culture media with purebred enlarged culturing;
2, preparation bacteria suspension: the bacteria suspension of preparing certain turbidity (cell concn) on request;
3, inoculation culture: bacterial suspension inoculation to micropore identification plate (Microplate), is cultivated certain hour;
4, obtain the result: the identification plate after will cultivating is put into the readout instrument reading, and software provides qualification result automatically.
Contain microbial population and quantitative measurement result such as table 1 in its mud, can find that in primary sludge microbial population is mainly based on bacterium, and successively decrease gradually with the variation in the stage of processing, and protozoon, metazoan begin showed increased, and fungi, algae occur under given conditions.
As above-mentioned microwave pasteurization principle as can be known, in sludge system, constitute microbial population survival pressure and the final factor of selecting and mainly comprise the type of final electron acceptor(EA) and utilize ability, obtainable matrix and utilizing ability, whether have the flocculation sediment characteristic, can survive at ambient temperature and growth, growth velocity height, whether having the growth suspending power matrix.Weigh from biomass, heterotrophic bacterium is the main bacteria seed (Pike and Curds, 1971) in the sludge microbe group bacterium.Heterotrophic bacterium utilizes the organism in the sewage, carries out the growth of self, thereby the amount of organic pollutant is reduced.Microbial population breeding, the alternately situation that increases, disappears occur, and are to change with envrionment conditionss such as the nutritional condition in the mud (kind of waste water, chemical constitution, concentration), temperature, oxygen supply, pH, then can cause predominantly bacteria population (dominant bacteria) to change.
Microbial population generation alternation procedure, variation has taken place in the condition and the character that have reflected mud, dead microorganism is flocculated again and combines, or and become the food chain of another kind of microorganism, cause its metabolism and more increased the weight of the complex construction of mud, and in this process because action of microorganisms is aided with combination reaction, generation is such as more poisonous and harmful elements such as foreign odor flavor, the also more difficult realization of sludge dewatering.
Table 1 is taken from husky certain sludge of sewage treatment plants of Hunan star and is contained microbial population and quantitative measurement
(annotate: "--" is illustrated in this sub-sampling, and undetermined goes out temporarily, may exist in the other times section.)
Based on this, microwave pasteurization experimentizes to primary sludge described in employing the present invention, and experimental procedure is as follows:
Get primary sludge 2.0Kg and place beaker, add water 0.5L, add mass concentration and be 93% technical grade sulfuric acid 0.04L, stir evenly, send in the microwave device and heat, make slurry temperature reach certain temperature and keep certain hour.Test for continuous 3 times by differing temps and time conditions, slurries are measured as stated above, measurement result shows that microwave pasteurization is main relevant to temperature table 2.
Then slurries are carried out solid-liquid separation, and wash, get dewatered sludge slag and new slurries with 0.5L water.
The dewatered sludge slag that obtains, weight in wet base and the dry weight such as the table 3 of the dewatered sludge slag that continuous 3 experiments obtain.This dewatered sludge slag can according to local reality voluntarily deep processing manufacture a product, also can be sent to other processing bases and manufacture a product.
New slurries are regulated pH value to 6.0~8.5 with lime, and new slurries can be used as the cycling use of water reuse to mud acidifying slurrying liquid and mechanical filter separating, washing, the Sewage treatment systems that the remaining new slurries of part can be sent sewage work back to after the reuse.
The microbial population number change is measured before and after the table 2 primary sludge microwave pasteurization
Figure BSA00000267444400071
The weight in wet base and the dry weight (Kg) of the dewatered sludge slag that continuous 3 experiments of table 3 obtain
Sequence number The primary sludge source The primary sludge weight in wet base Dewatered sludge slag weight in wet base Dewatered sludge slag dry weight
1 Sewage work 2.0 0.722 0.431
2 Sewage work 2.0 0.713 0.425
3 Sewage work 2.0 0.687 0.424
By table 2 and table 3 as can be known, primary sludge has been realized effective germ-resistant purpose after adopting present method to handle, also realized simultaneously the purpose of high-efficiency dehydration, the dewatered sludge slag that produces, can according to local reality voluntarily deep processing manufacture a product, also can be sent to other processing bases and manufacture a product.
More than show and described ultimate principle of the present invention and principal character and advantage of the present invention.The technician of the industry should understand; the present invention is not restricted to the described embodiments; that describes in the foregoing description and the specification sheets just illustrates principle of the present invention; without departing from the spirit and scope of the present invention; the present invention also has various changes and modifications, and these changes and improvements all fall in the claimed scope of the invention.The claimed scope of the present invention is defined by appending claims and equivalent thereof.

Claims (1)

1. the method for effective sterilization of primary sludge and high-efficiency dehydration is characterized in that, may further comprise the steps:
(1) primary sludge acidification: the primary sludge of getting urban wastewater treatment firm, water ratio 97%~99.5%, add entry in the mass ratio of water and primary sludge in 0.2: 1~1: 1 ratio, the mass ratio that in mass concentration is 93%~98% technical grade sulfuric acid and primary sludge adds technical grade sulfuric acid in 0.02: 0.1~0.1: 1 ratio, after stirring 5~10min, add the technical grade hydrogen peroxide in the mass ratio of concentration 27.5%~35% technical grade hydrogen peroxide and primary sludge in 0.02: 0.1~0.1: 1 ratio, stirring reaction 5~10min makes slurries;
(2) microwave pasteurization: slurries are heated to 30 ℃~90 ℃, heat-up time 15~90min;
(3) mechanical filter: the slurries after the microwave heating treatment are carried out solid-liquid separation and wash with water, dewatered sludge slag and new slurries, the mass ratio of washing water consumption and primary sludge 0.3: 1~1: 1;
(4) new slurries are regulated pH value to 6.0~8.5 with lime, and new slurries can be used as the cycling use of water reuse to mud acidifying slurrying liquid and mechanical filter separating, washing, and the Sewage treatment systems that the remaining new slurries of part can be sent sewage work back to after the reuse gets final product.
CN2010102800959A 2010-09-14 2010-09-14 Method for effective sterilization and efficient hydration of primary sludge Expired - Fee Related CN101962255B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2010102800959A CN101962255B (en) 2010-09-14 2010-09-14 Method for effective sterilization and efficient hydration of primary sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2010102800959A CN101962255B (en) 2010-09-14 2010-09-14 Method for effective sterilization and efficient hydration of primary sludge

Publications (2)

Publication Number Publication Date
CN101962255A true CN101962255A (en) 2011-02-02
CN101962255B CN101962255B (en) 2012-07-04

Family

ID=43515347

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2010102800959A Expired - Fee Related CN101962255B (en) 2010-09-14 2010-09-14 Method for effective sterilization and efficient hydration of primary sludge

Country Status (1)

Country Link
CN (1) CN101962255B (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102432145A (en) * 2011-11-09 2012-05-02 长沙华清泰污泥处理科技有限公司 Tannery sludge treatment method for sterilizing, deodorizing and removing heavy metals
CN102491551A (en) * 2011-11-22 2012-06-13 浙江嘉澳环保科技股份有限公司 Treatment method for hydrogen peroxide-containing organic wastewater
CN103013613A (en) * 2012-12-24 2013-04-03 西安科技大学 Clean fuelization system and fuelization method for urban sludge
CN103708689A (en) * 2013-12-20 2014-04-09 湖南大学 Sterilization, deodorization and deep-dehydration method for livestock excrements
CN106630506A (en) * 2016-07-01 2017-05-10 吴彦兴 Biological and physical degradation regeneration method for sludge without discharge (pollution) recovery
CN116282808A (en) * 2023-05-24 2023-06-23 江苏亿洲再生资源科技有限公司 Sludge uniform drying treatment equipment

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000026180A (en) * 1998-07-07 2000-01-25 Asano Koji Kk Method for composting organic sludge
CN101050037A (en) * 2007-04-04 2007-10-10 济南大陆机电有限公司 Method for treating paper making sewage
CN101580334A (en) * 2008-05-13 2009-11-18 中国科学院生态环境研究中心 Method for recovering sludge phosphorus from urban sewage treatment plant
CN101698561A (en) * 2009-10-23 2010-04-28 宁波工程学院 Silt pretreatment method for enhancing dehydration property and digestibility of silt

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000026180A (en) * 1998-07-07 2000-01-25 Asano Koji Kk Method for composting organic sludge
CN101050037A (en) * 2007-04-04 2007-10-10 济南大陆机电有限公司 Method for treating paper making sewage
CN101580334A (en) * 2008-05-13 2009-11-18 中国科学院生态环境研究中心 Method for recovering sludge phosphorus from urban sewage treatment plant
CN101698561A (en) * 2009-10-23 2010-04-28 宁波工程学院 Silt pretreatment method for enhancing dehydration property and digestibility of silt

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102432145A (en) * 2011-11-09 2012-05-02 长沙华清泰污泥处理科技有限公司 Tannery sludge treatment method for sterilizing, deodorizing and removing heavy metals
CN102491551A (en) * 2011-11-22 2012-06-13 浙江嘉澳环保科技股份有限公司 Treatment method for hydrogen peroxide-containing organic wastewater
CN103013613A (en) * 2012-12-24 2013-04-03 西安科技大学 Clean fuelization system and fuelization method for urban sludge
CN103708689A (en) * 2013-12-20 2014-04-09 湖南大学 Sterilization, deodorization and deep-dehydration method for livestock excrements
CN106630506A (en) * 2016-07-01 2017-05-10 吴彦兴 Biological and physical degradation regeneration method for sludge without discharge (pollution) recovery
CN106630506B (en) * 2016-07-01 2019-09-13 吴彦兴 Biological and physical degradation regeneration method for sludge recycling without pollution discharge
CN116282808A (en) * 2023-05-24 2023-06-23 江苏亿洲再生资源科技有限公司 Sludge uniform drying treatment equipment
CN116282808B (en) * 2023-05-24 2023-10-20 江苏亿洲再生资源科技有限公司 Sludge uniform drying treatment equipment

Also Published As

Publication number Publication date
CN101962255B (en) 2012-07-04

Similar Documents

Publication Publication Date Title
CN101962255B (en) Method for effective sterilization and efficient hydration of primary sludge
Al-Wasify et al. Biodegradation of dairy wastewater using bacterial and fungal local isolates
Forster-Carneiro et al. Mesophilic anaerobic digestion of sewage sludge to obtain class B biosolids: Microbiological methods development
Lund et al. Inactivation of virus during anaerobic digestion of manure in laboratory scale biogas reactors
Xing et al. A comparative study of synchronous treatment of sewage and sludge by two vermifiltrations using an epigeic earthworm Eisenia fetida
CN104071951B (en) A kind of fishpond cultivating wastewater purification technique and device thereof
CN108998386A (en) A kind of phagocytosis type bacterium applied to deeply dehydrating sludge
Patil et al. Conversion of organic biomedical waste into potential fertilizer using isolated organisms from cow dung for a cleaner environment
CN109796113A (en) A kind of sludge and derivative manufacturing method of high speed processing moisture content 80 percent
Song et al. Effect of Aeolosoma hemprichi on excess activated sludge reduction
Lu et al. Cultivation of Spirulina platensis using raw piggery wastewater for nutrients bioremediation and biomass production: effect of ferrous sulfate supplementation
Liew et al. Microalgae cultivation in stabilized landfill leachate for simultaneous treatment and biomass production
JP2008178864A (en) Solid-liquid separation method for alcoholic beverage lees, and solid-liquid separation device therefor
CN105820976A (en) Sludge compost thermophilic microbial agent and application
CN106186617B (en) A kind of medicament and processing method handling municipal sludge
CN204224395U (en) Urban sewage treating device
CN204281502U (en) Waste disposal plant
Campos et al. Abatement of helminth eggs and bacterial and viral indicators in soil after land application of treated sludges
CN204224394U (en) Domestic living waste water treater
RU2644013C2 (en) Method for producing environmentally friendly mineral-organic fertilisers with methane fermentation at biogas stations
Singh et al. Sewage effluent: a potential nutrient source for microalgae
van den Berg et al. Harvesting Microalgal Biomass from a Cultured Algae-Based Wastewater Pond System
CN204224390U (en) For the equipment of Sewage Plant sewage disposal
JP2007326016A (en) Biological waste water treatment method
CN204224393U (en) Sewage Plant waste disposal plant

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
C56 Change in the name or address of the patentee

Owner name: HUNAN SINOKING SLUDGE TREATMENT TECHNOLOGY CO., LT

Free format text: FORMER NAME: CHANGSHA JIEXIANG ENVIRONMENTAL ENGINEERING CO., LTD.

CP01 Change in the name or title of a patent holder

Address after: Wanjiali Hunan province 410000 Changsha Yuhua District, two No. 18 Management Service Center office building four floor No. 455

Patentee after: Hunan Huaqing Thai Sludge Treatment Technology Co. Ltd.

Address before: Wanjiali Hunan province 410000 Changsha Yuhua District, two No. 18 Management Service Center office building four floor No. 455

Patentee before: Changsha Jiexiang Environmental Engineering Co., Ltd.

C56 Change in the name or address of the patentee
CP02 Change in the address of a patent holder

Address after: Yuelu District City, Yuelu province Hunan 410000 Changsha Street South Second Ring Road section of No. 518 building 3-2 No. 116 Metro sunshine 100

Patentee after: Hunan Huaqing Thai Sludge Treatment Technology Co. Ltd.

Address before: Wanjiali Hunan province 410000 Changsha Yuhua District, two No. 18 Management Service Center office building four floor No. 455

Patentee before: Hunan Huaqing Thai Sludge Treatment Technology Co. Ltd.

C17 Cessation of patent right
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20120704

Termination date: 20130914