CN104098174A - Production method for active carriers used in biological sewage denitrification - Google Patents

Production method for active carriers used in biological sewage denitrification Download PDF

Info

Publication number
CN104098174A
CN104098174A CN201410375065.4A CN201410375065A CN104098174A CN 104098174 A CN104098174 A CN 104098174A CN 201410375065 A CN201410375065 A CN 201410375065A CN 104098174 A CN104098174 A CN 104098174A
Authority
CN
China
Prior art keywords
carrier
corallite
ammonia nitrogen
production method
grams
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201410375065.4A
Other languages
Chinese (zh)
Inventor
李天源
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to CN201410375065.4A priority Critical patent/CN104098174A/en
Publication of CN104098174A publication Critical patent/CN104098174A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

The invention discloses a production method for active carriers used in sewage biological denitrification. The production method comprises the following steps: 1, selecting corallite bone black and plastic carriers; 2, conducting microbial carrier cultivation: artificially preparing wastewater, adding pond sludge into a container for mixing, adding corallite for aeration cultivation at 25-30 DEG C for 10-15 days, and adopting the Nessler's reagent method to detect ammonia nitrogen to show whether carrier bacteria generate or not; 3, conducting carrier enlarging cultivation: mixing cultivated nitrifying bacteria carriers with neosoma in a ratio of 1:3 for enlarging cultivation according to the carrier bacteria enlarging cultivation method; 4, completing the production when the removal rate of carrier ammonia nitrogen (8.0 mg/L) obtained is greater than 85%, and the nitrifying rate is greater than 8.0 kg/(m<3>.d) by adopting the method.

Description

A kind of production method of bio-denitrifying sewage active carrier
One, technical field
The present invention relates to a kind of production method of bio-denitrifying sewage active carrier.
Two, technical background
Polluted by nitrogen is to cause body eutrophication major reason, and the object of processing is to reduce nitrogen content.Water body denitrification method has physical adsorption, chemical reaction, coagulating sedimentation and biological denitrificaion etc., and biological denitrificaion is maximum with nitrated-denitrification combined utilization.Because remarkable, the simple to operate construction costs of the reliable effect of technology is low, do not cause secondary pollution.Be widely applied.
Adopt at present the method for biological denitrificaion to have A/O, A 2the technology that/O, SBR gather mutually with short distance nitration and Anammox, these are all the zoogloea of using microbe formation and the mud group of thread fungus and microfauna formation.Aspect experimental study, obtaining good result, still there is defect in various degree in the application of mass-producing.
Someone uses the fixedly bio-denitrification technology such as embedding, bio-carrier, material has biocycle and ball, porous insert, haydite, soft and elastic filler, the smooth surface that this class material has is unfavorable for that nitrifier adheres to and grows, and what have does not meet drinking water hygiene requirement, and overall rate of nitrification is not high.
Due to A/O and A 2/ O technique self exists carbon source competition, nitrated incomplete, heavy pond to float the factors such as mud, sludge bulking, mud Age ratio control, ammonia nitrogen qualified discharge inhuman meaning after denitrogenation.Water environment pollution can not get effectively administering and occurring eutrophication.Cast Some Lakes wawter bloom red tide of sea, cause many harm to industrial and agricultural production and people's life.
Biological denitrificaion is to utilize the effect in nitrogen cycle of nitrification and denitrification bacterium in physical environment.Low according to nitrifier capacity usage ratio, poor growth, the breeding cycle is long is obligate autotrophy bacterium, usings oxygen as final electron acceptor(EA) and obtain the needed energy of growth in oxidising process, can not on organic substratum, grow.The problem and the bio-denitrification technology requirement that based on this and sewage disposal, exist, the present invention is the nitrifier that screening one strain has efficient denitrification ability, being cultivated domestication increases bacterium and depends on the carrier of suitable growth breeding, growth and breeding under artificial condition, making it is that maximum rate of nitrification is brought into play in Engineering Service.
Three, summary of the invention
The object of the present invention is to provide a kind of production method of bio-denitrifying sewage active carrier, the production method of this active carrier is to be undertaken by following process:
1, select materials: 1. select high-quality corallite shell and bone black, granularity requirements 3-8mm; 2. plastic carrier is that corallite shell and bone black are crushed to separately and can merge mutually and be processed into thread or velutinate carrier with plastics;
2, carrier carries bacterium and cultivates: artificial wastewater's preparation, with 2 liters with 2.0 grams of upper container chlorination ammonia, 1200 milliliters of ordinary waters, with sodium carbonate adjust pH 7.5-8.0, add 200 grams, settling tank mud, be mixed, add 1000 grams of corallites, under the condition of 25-30 ℃, aeration is cultivated 10-15 days.If ammonia nitrogen is reduced to zero continuing and added ammonium chloride, pH value adds sodium carbonate lower than 7.0 and is adjusted to regulation.By nessler reagent colorimetric determination ammonia nitrogen situation, to judge whether carry thalline generates with qualified;
3, carrier enlarged culturing: wash away mud by cultivating nitrifier carrier appropriate and domestication, in mixing with 1: 3 ratio of corallite, carry bacterium cultural method expanding species by carrier;
Clearance > 85% when the carrier ammonia nitrogen that 4, this law is produced is 8.0mg/L.The nitrated rate of volume is greater than 8.0kg/ (m 3.d).
Five, embodiment
Embodiment 1:
A kind of production method of bio-denitrifying sewage active carrier is undertaken by following process:
1, select materials: 1. select high-quality corallite, granularity requirements 3-8mm;
2, carrier carries bacterium and cultivates: artificial wastewater's preparation, with 2 liters with 2.0 grams of upper container chlorination ammonia, 1200 milliliters of ordinary waters, with sodium carbonate adjust pH 7.5-8.0, add 200 grams, settling tank mud, be mixed, add 1000 grams of corallites, under the condition of 25-30 ℃, aeration is cultivated 10-15 days.If ammonia nitrogen is reduced to zero continuing and added ammonium chloride, pH value adds sodium carbonate lower than 7.0 and is adjusted to regulation.By nessler reagent colorimetric determination ammonia nitrogen situation, to judge whether carry thalline generates with qualified;
3, carrier enlarged culturing: wash away mud by cultivating nitrifier carrier appropriate and domestication, in mixing with 1: 3 ratio of corallite, carry bacterium cultural method expanding species by carrier;
Clearance > 85% when the carrier ammonia nitrogen that 4, this law is produced is 8.0mg/L.The nitrated rate of volume is greater than 8.0kg/ (m 3.d).
Embodiment 2:
A kind of production method of bio-denitrifying sewage active carrier is undertaken by following process:
1, select materials: 1. select high-quality bone black, granularity requirements 3-8mm; ;
2, carrier carries bacterium and cultivates: artificial wastewater's preparation, with 2 liters with 2.0 grams of upper container chlorination ammonia, 1200 milliliters of ordinary waters, with sodium carbonate adjust pH 7.5-8.0, add 200 grams, settling tank mud, be mixed, add 1000 grams of bone black, under the condition of 25-30 ℃, aeration is cultivated 10-15 days.If ammonia nitrogen is reduced to zero continuing and added ammonium chloride, pH value adds sodium carbonate lower than 7.0 and is adjusted to regulation.By nessler reagent colorimetric determination ammonia nitrogen situation, to judge whether carry thalline generates with qualified;
3, carrier enlarged culturing: wash away mud by cultivating nitrifier carrier appropriate and domestication, in mixing with 1: 3 ratio of corallite, carry bacterium cultural method expanding species by carrier;
Clearance > 85% when the carrier ammonia nitrogen that 4, this law is produced is 8.0mg/L.The nitrated rate of volume is greater than 8.0kg/ (m 3.d).
Embodiment 3:
A kind of production method of bio-denitrifying sewage active carrier is undertaken by following process:
1, select materials: 1. selecting high-quality plastics carrier is that corallite shell and bone black are crushed to separately and can merge mutually and be processed into thread or velutinate carrier with plastics;
2, carrier carries bacterium and cultivates: artificial wastewater's preparation, with 2 liters with 2.0 grams of upper container chlorination ammonia, 1200 milliliters of ordinary waters, with sodium carbonate adjust pH 7.5-8.0, add 200 grams, settling tank mud, be mixed, add 1000 grams of plastic carriers, under the condition of 25-30 ℃, aeration is cultivated 10-15 days.If ammonia nitrogen is reduced to zero continuing and added ammonium chloride, pH value adds sodium carbonate lower than 7.0 and is adjusted to regulation.By nessler reagent colorimetric determination ammonia nitrogen situation, to judge whether carry thalline generates with qualified;
3, carrier enlarged culturing: wash away mud by cultivating nitrifier carrier appropriate and domestication, in mixing with 1: 3 ratio of corallite, carry bacterium cultural method expanding species by carrier;
Clearance > 85% when the carrier ammonia nitrogen that 4, this law is produced is 8.0mg/L.The nitrated rate of volume is greater than 8.0kg/ (m 3.d).

Claims (1)

1. a production method for bio-denitrifying sewage active carrier, is characterized in that: the production method of this active carrier is undertaken by following process:
A, select materials: 1. select high-quality corallite shell and bone black, granularity requirements 3-8mm; 2. plastic carrier is that corallite shell and bone black are crushed to separately and can merge mutually and be processed into thread or velutinate carrier with plastics;
B, carrier carry bacterium to be cultivated: artificial wastewater's preparation, with 2 liters with 2.0 grams of upper container chlorination ammonia, 1200 milliliters of ordinary waters, with sodium carbonate adjust pH 7.5-8.0, add 200 grams, settling tank mud, be mixed, add 1000 grams of corallites, under the condition of 25-30 ℃, aeration is cultivated 10-15 days.If ammonia nitrogen is reduced to zero continuing and added ammonium chloride, pH value adds sodium carbonate lower than 7.0 and is adjusted to regulation.By nessler reagent colorimetric determination ammonia nitrogen situation, to judge whether carry thalline generates with qualified;
C, carrier enlarged culturing: by cultivating nitrifier carrier appropriate and domestication, wash away mud, in mixing with 1: 3 ratio of corallite, by carrier, carry bacterium cultural method expanding species;
Clearance > 85% when the carrier ammonia nitrogen that D, this law are produced is 8.0mg/L.The nitrated rate of volume is greater than 8.0kg/ (m 3.d).
CN201410375065.4A 2014-07-31 2014-07-31 Production method for active carriers used in biological sewage denitrification Pending CN104098174A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410375065.4A CN104098174A (en) 2014-07-31 2014-07-31 Production method for active carriers used in biological sewage denitrification

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410375065.4A CN104098174A (en) 2014-07-31 2014-07-31 Production method for active carriers used in biological sewage denitrification

Publications (1)

Publication Number Publication Date
CN104098174A true CN104098174A (en) 2014-10-15

Family

ID=51666770

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410375065.4A Pending CN104098174A (en) 2014-07-31 2014-07-31 Production method for active carriers used in biological sewage denitrification

Country Status (1)

Country Link
CN (1) CN104098174A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107840443A (en) * 2016-09-20 2018-03-27 李蕴凯 The method and device of sewage disposal second pond ammonia nitrogen is removed with tower active carrier
CN109912015A (en) * 2019-04-17 2019-06-21 江西夏氏春秋环境股份有限公司 A kind of biological denitrification process of livestock breeding wastewater

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1533989A (en) * 2003-04-02 2004-10-06 日立工程设备建设株式会社 Nitrating method and device and waste water processor
CN101767919A (en) * 2010-01-11 2010-07-07 中国水产科学研究院黄海水产研究所 Microbial purification facility and method for water quality of intensive culture system of pond
KR100984154B1 (en) * 2010-01-27 2010-09-30 주식회사 그린기술산업 Water treatment facilities
CN103420481A (en) * 2013-08-19 2013-12-04 北京工业大学 Anaerobic ammonia oxidized coupled heterotrophic denitrifying denitrification method

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1533989A (en) * 2003-04-02 2004-10-06 日立工程设备建设株式会社 Nitrating method and device and waste water processor
CN101767919A (en) * 2010-01-11 2010-07-07 中国水产科学研究院黄海水产研究所 Microbial purification facility and method for water quality of intensive culture system of pond
KR100984154B1 (en) * 2010-01-27 2010-09-30 주식회사 그린기술산업 Water treatment facilities
CN103420481A (en) * 2013-08-19 2013-12-04 北京工业大学 Anaerobic ammonia oxidized coupled heterotrophic denitrifying denitrification method

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
赵倩等: "碳氮比对滤料除氨氮能力的影响试验研究", 《海洋环境科学》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107840443A (en) * 2016-09-20 2018-03-27 李蕴凯 The method and device of sewage disposal second pond ammonia nitrogen is removed with tower active carrier
CN109912015A (en) * 2019-04-17 2019-06-21 江西夏氏春秋环境股份有限公司 A kind of biological denitrification process of livestock breeding wastewater

Similar Documents

Publication Publication Date Title
CN107082536B (en) Breeding wastewater treatment process
CN106242045B (en) A kind of aerobic particle mud fast culture process
Li et al. Efficient ammonia removal in recirculating vertical flow constructed wetlands: Complementary roles of anammox and denitrification in simultaneous nitritation, anammox and denitrification process
CA2374537A1 (en) Method of high-concentration culture of nitrifying bacteria or denitrifying bacteria contained in activated sludge, culture promoter to be used in high-concentration culture method of nitrifying bacteria, and mehtod of weight loss treatment of activated sludge
CN104710006A (en) Improved A2/O biological membrane reactor capable of synchronously removing carbon, nitrogen and phosphorus, and operation method thereof
Huynh et al. Application of CANON process for nitrogen removal from anaerobically pretreated husbandry wastewater
CN106635923A (en) Method for preparing high-density salt-tolerant denitrifying bacterium agent applicable to wastewater treatment
Li et al. Performance of integrated ecological treatment system for decentralized rural wastewater and significance of plant harvest management
CN104232546A (en) Construction method and application of immobilized biological bacterium agent for micro-polluted water source
CN109851163B (en) Slow-flow small-watershed algae removal and control method
CN101955885A (en) High-efficiency denitrification mixed bacterial agent and application thereof
We et al. Influence of static mixer on the development of aerobic granules for the treatment of low-medium strength domestic wastewater
CN110240262A (en) A method of not only retaining ammonia nitrogen in livestock and poultry cultivation biological wastewater treatment process but also had removed antibiotic
CN104611279B (en) A kind of red city Rhodococcus sp LH N13 and its microbial bacterial agent and purposes
CN103740617A (en) Composite microbial agent, preparation method thereof and salty sewage treatment method
CN109052834A (en) A kind of administering method of eutrophication water
CN112158962A (en) Microbial water body in-situ treatment flora purification body and sewage treatment method adopting same
CN103626302B (en) The sewage water treatment method that a kind of denitrogenation dephosphorizing bacterial classification On-line testing is cultivated and tamed
Muñoz-Palazon et al. Novel application of aerobic granular biofilm systems for treating nitrate-polluted groundwater at low temperature: Microbial community and performance
CN105585133A (en) Bio-denitrification method for high-salt-content wastewater discharged from catalyst production process
CN109912015A (en) A kind of biological denitrification process of livestock breeding wastewater
CN104098174A (en) Production method for active carriers used in biological sewage denitrification
CN109055252A (en) A kind of heterotrophic nitrification-aerobic denitrification complex microorganism preparations and preparation method thereof
CN110577335A (en) Method for promoting food chain operation and accelerating water environment treatment
CN102491612A (en) Device and treatment method for digesting sludge with microorganism and microfauna

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20141015