CN104445642A - Urban sewage treatment composite material as well as preparation method and application thereof - Google Patents

Urban sewage treatment composite material as well as preparation method and application thereof Download PDF

Info

Publication number
CN104445642A
CN104445642A CN201410744995.2A CN201410744995A CN104445642A CN 104445642 A CN104445642 A CN 104445642A CN 201410744995 A CN201410744995 A CN 201410744995A CN 104445642 A CN104445642 A CN 104445642A
Authority
CN
China
Prior art keywords
sewage treatment
raw material
matrix material
diatomite
municipal sewage
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
CN201410744995.2A
Other languages
Chinese (zh)
Other versions
CN104445642B (en
Inventor
惠阳
吴静
苏珊珊
卢勇
黎明
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.)
WUHAN LVYANG ENVIRONMENTAL PROTECTION Co Ltd
Original Assignee
WUHAN LVYANG ENVIRONMENTAL PROTECTION 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 WUHAN LVYANG ENVIRONMENTAL PROTECTION Co Ltd filed Critical WUHAN LVYANG ENVIRONMENTAL PROTECTION Co Ltd
Priority to CN201410744995.2A priority Critical patent/CN104445642B/en
Publication of CN104445642A publication Critical patent/CN104445642A/en
Application granted granted Critical
Publication of CN104445642B publication Critical patent/CN104445642B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The invention discloses an urban sewage treatment composite material as well as a preparation method and application thereof. The urban sewage treatment composite material is prepared from rice hull, diatomite, polyaluminum chloride and ferment bacteria according to certain weight percentages. The preparation method comprises the following steps: A, uniformly mixing the rice hull and ferment bacteria, and naturally stacking and fermenting for two weeks to obtain a mixed raw material, wherein the fermentation temperature is 65-70 DEG C; B, when in use, uniformly mixing according to a condition that the weight ratio of the mixed raw material to water to brown sugar is equal to 1:0.3:0.01, fermenting for 110-130 minutes for later use, and ensuring that the water temperature of treated sewage is less than 10 DEG C; and C, uniformly mixing the mixed raw material which is fermented for later use with diatomite and polyaluminum chloride according to weight percentages to obtain the composite material. The invention also relates to an application of the composite material in urban sewage treatment. By virtue of the synergistic effects of adsorption, flocculation and biological transformation, the problems that an existing urban sewage treatment system cannot be used for effectively removing some hardly-degradable organic matters and soluble pollutants such as phosphorus and nitrogen can be solved, and thus a condition that effluent can reach the first grade A standard which is superior to the national urban and town sewage discharge standard can be ensured.

Description

A kind of municipal sewage treatment matrix material and preparation method and application
Technical field
The present invention relates to field of municipal sewage treatment, be specifically related to a kind of municipal sewage treatment matrix material, also relate to a kind of preparation method of municipal sewage treatment matrix material simultaneously, also relate to a kind of purposes of municipal sewage treatment matrix material.
Background technology
In current domestic built, the municipal sewage plant that runs, adopt treatment process the most widely, materialization intensive treatment method, AB method FEOL, technology such as hydrolysis aerobic method FEOL and high loading activated sludge process etc. are selected in primary reinforcement process usually; Second-stage treatment technique, according to the scale of municipal sewage plant, selects activated sludge process, oxidation ditch process, SBR method, hydrolysis aerobic method, AB method and biological filter process; Secondary reinforcement treatment process then selects A/O method, A/A/O method.Object is intensified denitrification and dephosphorization effect while of removing carbon source pollutent, but these techniques in actual applications, due to the impact by factors such as the fluctuation of influent quality and running costs, still can not effectively remove nitrogen in sewage, phosphorus, pathogenic micro-organism, heavy metal and organic pollutant etc., especially to the soluble pollutants such as organism, phosphorus, nitrogen of some difficult degradations.Even if water outlet can be stablized reach national discharge water secondary standard, for storage lake, river and reservoir, water inlet is still bad five class water quality.As can be seen here, the raising day by day that propelling and National Pollutant reduction of discharging along with urbanization require, the raising of the emission standard of sewage work also must become trend.In existing municipal sewage treatment A/O technique, add new city sewage disposal matrix material, by absorption, flocculation and the synergy of bio-transformation, solve the soluble pollutants problem such as organism, phosphorus, nitrogen that existing urban sewage treatment system effectively can not remove some difficult degradations, ensure that water outlet reaches and be better than national town sewage emission standard one-level A standard.
Summary of the invention
In order to solve above technical problem, the object of the invention is to there are provided a kind of municipal sewage treatment matrix material, the rice hulls of fermenting and diatomite have efficient adsorptivity, the pollutents such as energy active adsorption dissolved organic matter, phosphorus, nitrogen; Polymerize aluminum chloride has efficient flocculating effect, effectively can flocculate, precipitate the pollutents such as SS, organism, phosphorus, nitrogen; The microbiobacterial agent that matrix material adds effectively can decompose, transform nitrogen.The removal efficiency of its SS, chemical oxygen demand (COD), total nitrogen, total phosphorus and ammonia nitrogen can reach 94.3%, 92.8%, 92.9%, 96.7% and 96.2% respectively.
Another object of the present invention is the preparation method that there are provided a kind of municipal sewage treatment matrix material, easy to implement the method, easy and simple to handle, the rice hulls of fermenting contains the nutritive substances such as polysaccharide, crude fat and crude protein, necessary nutritive ingredient can be provided for microorganism, be convenient to the attachment of microorganism, there is stronger synchronous de-carbon, the effect of denitrogenation.Polymerize aluminum chloride has efficient flocculating effect, effectively can flocculate, precipitate the pollutents such as SS, organism, phosphorus, nitrogen; The microbiobacterial agent that matrix material adds effectively can decompose, transform nitrogen.
A further object of the invention there are provided the application of a kind of municipal sewage treatment matrix material in municipal sewage treatment, solve prior art and can not effectively remove the problems such as nitrogen in sewage, phosphorus, pathogenic micro-organism, heavy metal and organic pollutant, ensure that water outlet reaches and be better than national town sewage emission standard one-level A standard.
A kind of municipal sewage treatment matrix material, it is made up of the weight percent of following raw material:
Raw material weight per-cent %
Rice hulls 56-75%
Diatomite 13-30%
Polymerize aluminum chloride 5.5-9.5%
Enzymatic microorganism 3.5-7.5%.
Described enzymatic microorganism: comprise subtilis, yeast, actinomycetes.
Described subtilis living bacteria count is 2,000,000,000/gram;
Described yeast living bacteria count is 3,500,000/gram;
Described actinomycetes living bacteria count is 3,000,000/gram.
Described enzymatic microorganism, subtilis, yeast, actinomycetes do not account for the weight percent of above-mentioned raw materials.
A kind of municipal sewage treatment matrix material, it is made up (preferable range) of the weight percent of following raw material:
Raw material weight per-cent %
Rice hulls 58-70%
Diatomite 15-25%
Polymerize aluminum chloride 5.8-7.8%
Enzymatic microorganism 5.6-7.1%.
A kind of municipal sewage treatment matrix material, it is made up (good scope) of the weight percent of following raw material:
Raw material weight per-cent %
Rice hulls 58-68%
Diatomite 16-24%
Polymerize aluminum chloride 6-7.5%
Enzymatic microorganism 5.7-6.4%.
A kind of municipal sewage treatment matrix material, it is made up (better scope) of the weight percent of following raw material:
Raw material weight per-cent %
Rice hulls 61-66%
Diatomite 20-23%
Polymerize aluminum chloride 6.6-7.2%
Enzymatic microorganism 5.8-6.7%.
A kind of municipal sewage treatment matrix material, it is made up (optimum range) of the weight percent of following raw material:
Raw material weight per-cent %
Rice hulls 63-65%
Diatomite 21-22%
Polymerize aluminum chloride 6.8-7%
Enzymatic microorganism 6.1-6.5%.
A kind of municipal sewage treatment matrix material, it is made up (optimum value) of the weight percent of following raw material:
Raw material weight per-cent %
Rice hulls 65%
Diatomite 20%
Polymerize aluminum chloride 8.5%
Enzymatic microorganism 6.5%.
A preparation method for municipal sewage treatment matrix material, the steps include:
A, rice hulls, enzymatic microorganism to be mixed, natural packing fermentation two weeks, acquisition mixing raw material; Leavening temperature scope is 65-70 DEG C; Described enzymatic microorganism comprises subtilis, yeast, actinomycetes; Subtilis living bacteria count is 2,000,000,000/gram, yeast living bacteria count is 3,500,000/gram, actinomycetes living bacteria count is 3,000,000/gram.
Press mixing raw material when B, use: water: the weight ratio mixing of brown sugar=1:0.3:0.01, ferment for subsequent use after 110-130 minute.If dispose of sewage, water temperature is lower than 10 DEG C;
C, by fermentation after mixing raw material for subsequent use mix by weight percentage with diatomite, polymerize aluminum chloride, acquisition matrix material.
The application of municipal sewage treatment matrix material in municipal sewage treatment, the steps include:
(1) press mixing raw material when using: water: the weight ratio mixing of brown sugar=1:0.3:0.01, ferment for subsequent use after 2 hours.If dispose of sewage, water temperature is lower than 10 DEG C, and this step can be omitted.
(2) add diatomite, polymerize aluminum chloride mixes, obtain matrix material.
(3) this matrix material is thrown in municipal sewage treatment A/O system O section, bring into use.Add-on is that sewage per ton adds 0.2-0.45Kg.
After employing municipal sewage treatment matrix material of the present invention, municipal effluent plant effluent reaches and is better than national town sewage emission standard one-level A standard.(method and standard detection according to GB 18918-2002 " urban wastewater treatment firm pollutant emission standard ").
The rice hulls of the fermentation that the present invention uses contains the nutritive substances such as polysaccharide, crude fat and crude protein, can provide necessary nutritive ingredient, be convenient to the attachment of microorganism, have stronger synchronous de-carbon, the effect of denitrogenation for microorganism.Polymerize aluminum chloride has efficient flocculating effect, effectively can flocculate, precipitate the pollutents such as SS, organism, phosphorus, nitrogen;
The subtilis that the present invention uses by larger molecular organicses a large amount of in sewage and obnoxious flavour (ammonia, hydrogen sulfide etc.), can be decomposed into small molecules (polypeptide, higher fatty acid etc.).Then, then be decomposed into more micromolecular organism (monose, disaccharides, lower fatty acid etc.), be finally decomposed into carbonic acid gas, nitrate and vitriol etc., effectively reduce COD, the BOD in water, make the amino nitrogen (NH in water body 3-N), nitroso-group nitrogen (NO 2-N) and sulfide concentration reduction.Actinomycetes energy decomposing protein, Mierocrystalline cellulose and organism, the taste offseted except water body also has certain effect.Yeast effectively can decompose gas chromatography and grease etc., can remove COD and BOD in water, and water quality is improved.Also there is synergy between each bacterial classification, the monose that subtilis and actinomycetes degradation of organic substances generate and disaccharides etc. can be supplied to yeast and utilize, and yeast can play its Decomposition in sewage, make up subtilis and actinomycetic deficiency.
The present invention compared with prior art, has the following advantages and effect:
The rice hulls of 1, fermenting and diatomite have efficient adsorptivity, the pollutents such as energy active adsorption dissolved organic matter, phosphorus, nitrogen; Polymerize aluminum chloride has efficient flocculating effect, effectively can flocculate, precipitate the pollutents such as SS, organism, phosphorus, nitrogen; The microbiobacterial agent that matrix material adds effectively can decompose, transform nitrogen.The removal efficiency of its SS, chemical oxygen demand (COD), total nitrogen, total phosphorus and ammonia nitrogen can reach 94.3%, 92.8%, 92.9%, 96.7 and 96.2% respectively.
2, the preparation method of a kind of municipal sewage treatment matrix material of the present invention is easy, easy and simple to handle.The rice hulls of fermenting contains the nutritive substances such as polysaccharide, crude fat and crude protein, can provide necessary nutritive ingredient, be convenient to the attachment of microorganism, have stronger synchronous de-carbon, the effect of denitrogenation for microorganism.
This matrix material is thrown in in municipal sewage treatment A/O system O section by the present invention, by absorption, flocculation and the synergy of bio-transformation, solve the soluble pollutants problem such as organism, phosphorus, nitrogen that existing urban sewage treatment system effectively can not remove some difficult degradations, ensure that water outlet reaches and be better than national town sewage emission standard one-level A standard.
Embodiment
embodiment 1:
A kind of municipal sewage treatment matrix material, it is made up of the weight percent of following raw material:
Raw material weight per-cent %
Rice hulls 65%
Diatomite 20%
Polymerize aluminum chloride 8.5%
Enzymatic microorganism 6.5%.
A preparation method for municipal sewage treatment matrix material, the steps include:
A, rice hulls, enzymatic microorganism are mixed, natural packing ferments two weeks (14 days), obtains mixing raw material; Leavening temperature scope is 65 or 67 or 69 or 70 DEG C; Described enzymatic microorganism comprises subtilis, yeast, actinomycetes; Subtilis living bacteria count is 2,000,000,000/gram, yeast living bacteria count is 3,500,000/gram, actinomycetes living bacteria count is 3,000,000/gram.
Press mixing raw material when B, use: water: the weight ratio mixing of brown sugar=1:0.3:0.01, ferment for subsequent use after 110 or 115 or 119 or 123 or 125 or 128 or 130 minutes.Water temperature of disposing of sewage is lower than 10 DEG C;
C, by fermentation after mixing raw material for subsequent use mix by weight percentage with diatomite, polymerize aluminum chloride, acquisition matrix material.
Does is what relation problem: B and C?
Described diatomite, polymerize aluminum chloride are all purchased in market.
A kind of municipal sewage treatment matrix material, it is made up of the raw material of following weight percent:
Raw material and embodiment 1 2 3 4 5
Rice hulls 64% 67% 66% 59% 65%
Diatomite 23% 20% 24% 28% 20%
Polymerize aluminum chloride 7% 6% 6.5% 7.4% 8.5%
Enzymatic microorganism 6% 7% 3.5% 5.6% 6.5%
Amount to 100 100 100 100 100
Its preparation process is identical with embodiment 1.
embodiment 10:
The application of municipal sewage treatment matrix material in municipal sewage treatment, the steps include:
(1) press mixing raw material when using: water: the weight ratio mixing of brown sugar=1:0.3:0.01, ferment for subsequent use after 2 hours.If dispose of sewage, water temperature is lower than 10 DEG C, and this step can be omitted.
(2) mixing raw material mixes by weight percentage with diatomite, polymerize aluminum chloride, obtains matrix material.
(3) this matrix material is thrown in municipal sewage treatment A/O system O section, bring into use.Add-on is that sewage per ton adds 0.2-0.45Kg.
After employing municipal sewage treatment matrix material of the present invention, municipal effluent plant effluent reaches and is better than national town sewage emission standard one-level A standard.(method and standard detection according to GB 18918-2002 " urban wastewater treatment firm pollutant emission standard ").

Claims (8)

1. a municipal sewage treatment matrix material, it is made up of the raw material of following weight percent:
Raw material %
Rice hulls 56-75%
Diatomite 13-30%
Polymerize aluminum chloride 5.5-9.5%
Enzymatic microorganism 3.5-7.5%;
Described enzymatic microorganism: comprise subtilis, yeast, actinomycetes;
Described subtilis living bacteria count is 2,000,000,000/gram;
Described yeast living bacteria count is 3,500,000/gram;
Described actinomycetes living bacteria count is 3,000,000/gram.
2. a kind of municipal sewage treatment matrix material according to claim 1, is characterized in that:
Raw material %
Rice hulls 58-70%
Diatomite 15-25%
Polymerize aluminum chloride 5.8-7.8%
Enzymatic microorganism 5.6-7.1%.
3. a kind of municipal sewage treatment matrix material according to claim 1, is characterized in that:
Raw material %
Rice hulls 58-68%
Diatomite 16-24%
Polymerize aluminum chloride 6-7.5%
Enzymatic microorganism 5.7-6.4%.
4. a kind of municipal sewage treatment matrix material according to claim 1, is characterized in that:
Raw material %
Rice hulls 61-66%
Diatomite 20-23%
Polymerize aluminum chloride 6.6-7.2%
Enzymatic microorganism 5.8-6.7%.
5. a kind of municipal sewage treatment matrix material according to claim 1, is characterized in that:
Raw material %
Rice hulls 63-65%
Diatomite 21-22%
Polymerize aluminum chloride 6.8-7%
Enzymatic microorganism 6.1-6.5%.
6. a kind of municipal sewage treatment matrix material according to claim 1, is characterized in that:
Raw material %
Rice hulls 65%
Diatomite 20%
Polymerize aluminum chloride 8.5%
Enzymatic microorganism 6.5%.
7. the preparation method of a kind of municipal sewage treatment matrix material according to claim 1, the steps include:
A, rice hulls, enzymatic microorganism to be mixed, natural packing fermentation two weeks, acquisition mixing raw material; Leavening temperature scope is 65-70 DEG C; Described enzymatic microorganism comprises subtilis, yeast, actinomycetes; Subtilis living bacteria count is 2,000,000,000/gram, yeast living bacteria count is 3,500,000/gram, actinomycetes living bacteria count is 3,000,000/gram;
Press mixing raw material when B, use: water: the weight ratio mixing of brown sugar=1:0.3:0.01, ferment for subsequent use after 110-130 minute, water temperature of disposing of sewage is lower than 10 DEG C;
C, by fermentation after mixing raw material for subsequent use mix by weight percentage with diatomite, polymerize aluminum chloride, acquisition matrix material.
8. the application of a kind of municipal sewage treatment matrix material according to claim 1 in municipal sewage treatment; The steps include:
(1) press mixing raw material when using: water: the weight ratio mixing of brown sugar=1:0.3:0.01, ferment for subsequent use after 2 hours, water temperature of disposing of sewage is lower than 10 DEG C;
(2) mixing raw material mixes by weight percentage with diatomite, polymerize aluminum chloride, obtains matrix material;
(3) thrown in by this matrix material in municipal sewage treatment A/O system O section, bring into use, add-on is that sewage per ton adds 0.2-0.45Kg.
CN201410744995.2A 2014-12-09 2014-12-09 A kind of municipal sewage treatment composite and preparation method and application Expired - Fee Related CN104445642B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410744995.2A CN104445642B (en) 2014-12-09 2014-12-09 A kind of municipal sewage treatment composite and preparation method and application

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410744995.2A CN104445642B (en) 2014-12-09 2014-12-09 A kind of municipal sewage treatment composite and preparation method and application

Publications (2)

Publication Number Publication Date
CN104445642A true CN104445642A (en) 2015-03-25
CN104445642B CN104445642B (en) 2016-07-06

Family

ID=52892500

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410744995.2A Expired - Fee Related CN104445642B (en) 2014-12-09 2014-12-09 A kind of municipal sewage treatment composite and preparation method and application

Country Status (1)

Country Link
CN (1) CN104445642B (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105060502A (en) * 2015-08-05 2015-11-18 江苏淳盛农业科技发展有限公司 Domestic sewage purifying agent and preparation method thereof
CN106277366A (en) * 2016-09-29 2017-01-04 中国科学院水生生物研究所 A kind of pig-breeding wastewater treatment microbial microbial inoculum and preparation method and application
CN107285566A (en) * 2017-07-18 2017-10-24 王俊铎 A kind of city domestic sewage processing method
CN108298698A (en) * 2018-03-01 2018-07-20 南京誉弘腾环保科技有限公司 A kind of microbial water-purifying agent for river regulation
CN108503050A (en) * 2018-04-20 2018-09-07 侯文燕 A kind of method that microbe fermentation method prepares boiler water modifier
CN108650918A (en) * 2018-04-28 2018-10-16 内蒙古济世源环保生物科技有限公司 The method for improveing soil using composite enzyme
CN109319948A (en) * 2018-11-28 2019-02-12 福州宇澄环保工程设计有限公司 A kind of nano biological water purification agent
CN113912143A (en) * 2021-07-27 2022-01-11 大庆渤基科技开发有限公司 Enzyme water clarifier and application thereof

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1887748A (en) * 2006-01-24 2007-01-03 沈阳大学 Efficient ecological sewage treating promoter and its prepn process
CN103693754A (en) * 2013-12-20 2014-04-02 大连赛姆生物工程技术有限公司 Sea cucumber cultivation water quality repair agent capable of effectively reducing water turbidity, preparation method and use thereof
CN103922489A (en) * 2014-05-09 2014-07-16 四川清和科技有限公司 Microorganism composite flocculant coagulation bacterium application method

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1887748A (en) * 2006-01-24 2007-01-03 沈阳大学 Efficient ecological sewage treating promoter and its prepn process
CN103693754A (en) * 2013-12-20 2014-04-02 大连赛姆生物工程技术有限公司 Sea cucumber cultivation water quality repair agent capable of effectively reducing water turbidity, preparation method and use thereof
CN103922489A (en) * 2014-05-09 2014-07-16 四川清和科技有限公司 Microorganism composite flocculant coagulation bacterium application method

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105060502A (en) * 2015-08-05 2015-11-18 江苏淳盛农业科技发展有限公司 Domestic sewage purifying agent and preparation method thereof
CN105060502B (en) * 2015-08-05 2017-04-12 江苏淳盛农业科技发展有限公司 Domestic sewage purifying agent and preparation method thereof
CN106277366A (en) * 2016-09-29 2017-01-04 中国科学院水生生物研究所 A kind of pig-breeding wastewater treatment microbial microbial inoculum and preparation method and application
CN107285566A (en) * 2017-07-18 2017-10-24 王俊铎 A kind of city domestic sewage processing method
CN108298698A (en) * 2018-03-01 2018-07-20 南京誉弘腾环保科技有限公司 A kind of microbial water-purifying agent for river regulation
CN108503050A (en) * 2018-04-20 2018-09-07 侯文燕 A kind of method that microbe fermentation method prepares boiler water modifier
CN108503050B (en) * 2018-04-20 2021-09-24 侯文燕 Method for preparing boiler water regulator by microbial fermentation method
CN108650918A (en) * 2018-04-28 2018-10-16 内蒙古济世源环保生物科技有限公司 The method for improveing soil using composite enzyme
CN109319948A (en) * 2018-11-28 2019-02-12 福州宇澄环保工程设计有限公司 A kind of nano biological water purification agent
CN109319948B (en) * 2018-11-28 2021-06-15 福州宇澄环保工程设计有限公司 Preparation method of nano biological water purifying agent
CN113912143A (en) * 2021-07-27 2022-01-11 大庆渤基科技开发有限公司 Enzyme water clarifier and application thereof

Also Published As

Publication number Publication date
CN104445642B (en) 2016-07-06

Similar Documents

Publication Publication Date Title
CN104445642B (en) A kind of municipal sewage treatment composite and preparation method and application
CN103910463B (en) Novel process for BC urban sewage treatment
CN103373759B (en) Method for denitrifying wastewater generated in process of producing FCC (fluid catalytic cracking) catalyst
CN109485157A (en) A kind of compounded carbons for sewage water denitrification and preparation method thereof and application method
CN106277366B (en) A kind of pig-breeding wastewater treatment microbial microbial inoculum and preparation method and application
CN102676433B (en) Pseudomonas capable of removing nitrogen and phosphorus synchronously at low temperature and application thereof
CN103803711A (en) Method for treating ammonia-nitrogen wastewater by using immobilized microorganism
CN104496031B (en) A kind of sewage disposal is held concurrently water plant planting matrix fill preparation method and application
CN101708923A (en) Denitrifying phosphorus and nitrogen removal method for wastewater with low carbon-phosphorus ratio
CN108070543A (en) It is a kind of to be suitable for preparations and application of the low C/N than the denitrogenation bacteria preparation of wastewater treatment
CN102583724B (en) Method for utilizing activated sludge, ozone and magnetic field to reduce sludge
CN102874957A (en) Method for processing liquid dung of pig farm through flocculation oxidizing resistance dimishing method
CN102358674A (en) Sewage treatment method capable of sludge quantitative reduction
CN101701197B (en) Novel microorganism flora mixture and mixed nutrient medium thereof
CN103613250B (en) A kind for the treatment of process of pickle wastewater
CN103043869A (en) Recycling sewage treatment equipment by utilizing automatic backflow reactor and sewage treatment method thereof
Baloch et al. Carbon and nitrogen removal in a granular bed baffled reactor
CN111003816B (en) Biochemical tail water biological denitrification method for inhibiting non-filamentous bacterium expansion
CN106219872B (en) The processing method and organic wastewater treating system of organic wastewater
CN101928068A (en) Method of all self-oxygen ammonia nitrogen removal by particle sludge
CN107445403A (en) A kind of method for cooperateing with processing landfill percolate and burning electricity generation factory percolate
Girard et al. A review of the environmental pollution originating from the piggery industry and of the available mitigation technologies: towards the simultaneous biofiltration of swine slurry and methane
CN101928067B (en) Culture method of aerobic denitrification particle sludge
CN103342438A (en) Sewage and sludge processing system
CN113292159B (en) Enhanced CFBR (circulating fluidized bed reactor) process applied to high ammonia nitrogen-containing wig wastewater treatment

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20160706

Termination date: 20191209