CN110342746A - A kind of paraquat production method for biologically treating wastewater - Google Patents

A kind of paraquat production method for biologically treating wastewater Download PDF

Info

Publication number
CN110342746A
CN110342746A CN201910660320.2A CN201910660320A CN110342746A CN 110342746 A CN110342746 A CN 110342746A CN 201910660320 A CN201910660320 A CN 201910660320A CN 110342746 A CN110342746 A CN 110342746A
Authority
CN
China
Prior art keywords
abr
sbr
stage
paraquat
waste water
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
CN201910660320.2A
Other languages
Chinese (zh)
Inventor
姚红樱
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 CN201910660320.2A priority Critical patent/CN110342746A/en
Publication of CN110342746A publication Critical patent/CN110342746A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
    • C02F1/56Macromolecular compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/101Sulfur compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/12Halogens or halogen-containing compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • C02F2101/163Nitrates
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • C02F2101/18Cyanides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • C02F2101/345Phenols
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/40Organic compounds containing sulfur
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • C02F2103/343Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the pharmaceutical industry, e.g. containing antibiotics
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C02F3/341Consortia of bacteria

Abstract

The invention discloses a kind of paraquats to produce method for biologically treating wastewater, and treatment effeciency is high, at low cost, while can be by bioanalysis reliable treatments paraquat waste water, and treatment effect is more excellent compared to traditional biological method.Specific step is as follows: (1) the civil construction stage by the present invention: requiring to build ABR, SBR biochemistry pool and mating structures, and pipe laying and equipment according to technique;(2) proprietary bio-carrier adds the stage: requiring to add proprietary bio-carrier to ABR and SBR according to technique;(3) the compound bacteria microorganism of EMO adds the activation stage: activating the microorganism of ABR and SBR respectively as requested, and adds to ABR and SBR;(4) tame the stage: ABR fills it up with waste water in pond, plays self-loopa, and SBR is added portionwise waste water and is aerated;(5) operation phase: after the completion of microbial acclimation, entire technique starts continuous operation, monitors the Inlet and outlet water index of each biochemistry pool daily, until meeting processing requirement completes a process flow.

Description

A kind of paraquat production method for biologically treating wastewater
Technical field
The present invention relates to a kind of processing methods of paraquat production waste water, for carrying out at biology to paraquat production waste water Reason purification.
Background technique
With the rapid development of agricultural, the type and dosage of pesticide are also increased rapidly, at this stage, major part used in China Pesticide belongs to organic agricultural chemicals, many have the characteristics that toxicity it is big, it is difficult decompose, a disaster of the agricultural chemicals waste water as water treatment field Topic.Currently used method has: biochemical treatment, incineration method, super oxidation etc.: conventional biochemical processing generally require tame for a long time it is micro- Biology, and effect is unstable, many pesticides cannot be decomposed thoroughly;Condition needed for incineration method is harsh, cost is excessively high, and also easily leakage has Malicious pernicious gas;Super oxidation the high requirements on the equipment, thus it is at high cost, and operating risk is larger, it is difficult to it is universal.
Traditional Biochemical method paraquat production waste water, with elasticity or the carrier of associativity, is led to using activated sludge The bacterium that anaerobic pond and aerobic tank are gradually cultivated is crossed, the organic matter in waste water is made to be decomposed and be purified.But by hundred The factors such as the withered production wastewater toxicity of grass is high, and hardly possible is decomposed influence, and simply so that such waste water is reached using bioanalysis Qualified discharge purpose.
For this purpose, we constantly seek a kind of technique improved for paraquat production wastewater biochemical processing, to reach The purpose of final waste water energy qualified discharge.
Summary of the invention
In view of the above-mentioned deficiencies in the prior art, the technical problem to be solved by the present invention is that it is raw to provide a kind of paraquat Method for biologically treating wastewater is produced, treatment effeciency is high, and it is at low cost, while can be by bioanalysis reliable treatments paraquat waste water, place It is more excellent compared to traditional biological method to manage effect.
In order to achieve the above object, the present invention is achieved by the following scheme:
A kind of paraquat production method for biologically treating wastewater, includes 5 steps: civil construction stage, proprietary bio-carrier Add the stage, the compound bacteria microorganism of EMO adds activation stage, domestication stage, operation phase;Specific step is as follows:
(1) it the civil construction stage: requires to build ABR, SBR biochemistry pool and mating structures, and installing pipe according to technique Road and equipment;
(2) proprietary bio-carrier adds the stage: requiring to add proprietary bio-carrier to ABR and SBR according to technique;
(3) the compound bacteria microorganism of EMO adds the activation stage: as requested respectively activate ABR and SBR microorganism, and to ABR and SBR are added;
(4) tame the stage: ABR fills it up with waste water in pond, plays self-loopa, and SBR is added portionwise waste water and is aerated;
(5) operation phase: after the completion of microbial acclimation, entire technique starts continuous operation, monitors each biochemistry pool daily Inlet and outlet water index, until meeting processing requirement completes a process flow.
As a kind of preferred embodiment of the invention: in the above method, influent COD is controlled within 1500mg/L, into The paraquat of water controls within 30mg/L.
As a kind of preferred embodiment of the invention: in the above method, being discharged COD≤240mg/L, paraquat≤1mg/ L has reached industrial wastewater discharge standard.
As a kind of preferred embodiment of the invention: in the above method, the compound bacteria microorganism of EMO only need to be added once, Without adding and rejuvenation;Bio-carrier only need to be added once.
The medicine have the advantages that
The present invention is by using EMO compound bacteria microbial technique and proprietary bio-carrier and ABR+SBR (such as Fig. 1) composition The biochemical treatment of EMO biochemical treatment system, influent COD control within 1500mg/L, and the paraquat of water inlet is controlled in 30mg/L Within, it is discharged COD≤240mg/L, is discharged paraquat≤1mg/L, up to 84%, paraquat removal rate reaches the COD removal rate of waste water 97%, reach industrial wastewater discharge standard, engineering practice shows the stability and operability of this process.
Detailed description of the invention
Fig. 1 is a kind of process flow chart of specific embodiment of the invention.
Specific embodiment
The specific embodiment of the invention is described with reference to the accompanying drawings and embodiments:
As shown in Figure 1, it illustrates a specific embodiment of the invention, as shown in Figure 1, the invention discloses a kind of uses Biochemical method paraquat produces the process of waste water, this method are as follows: by using EMO compound bacteria microbial technique and proprietary The biochemical treatment of the EMO biochemical treatment system of bio-carrier and ABR+SBR (such as Fig. 1) composition, influent COD are controlled in 1500mg/L Within, the COD removal rate of waste water is up to 84%, and ammonia nitrogen removal frank reaches 95%, and paraquat removal rate has reached Industry Waste up to 97% Water discharge standard, engineering practice show the stability and operability of this process.
Specifically, biochemistry of the present invention using EMO compound bacteria microbial technique and proprietary bio-carrier and ABR+SBR composition Processing system.The COD of water inlet is controlled within 1500mg/L, and paraquat controls within 30mg/L, is discharged COD≤240mg/L, Paraquat≤1mg/L has reached industrial wastewater discharge standard;
The compound bacteria microorganism of EMO of the invention is only with once adding, without adding and rejuvenation;Bio-carrier is proprietary biology Carrier and only with once adding.
To sum up, the present invention relates to a kind of technical fields of paraquat production biological process of wastewater treatment method, more particularly to A kind of paraquat by using EMO compound bacteria microbial technique and the biologic treating technique of proprietary bio-carrier and ABR+SBR The method for producing biological process of wastewater treatment;The purpose of the invention is to overcome the prior art, provide one kind hundred grass The method of withered production biochemical treatment process for wastewater, the method which produces biochemical treatment process for wastewater are multiple by using EMO The biochemical treatment system of combined bacteria microbial technique and proprietary bio-carrier and ABR+SBR composition, reaches the COD removal rate of waste water 84%, ammonia nitrogen removal frank reaches 95%, and paraquat removal rate is up to 97%, and most of organic matter is degraded and reached in waste water Industrial wastewater discharge standard.
Sewage Biological Treatment of the invention fully relies on the effect of microorganism to purify waste water, therefore the microorganism in sewage Whether type whether complete (for pollutant to be dealt with), quantity just become the condition of most critical enough.Only by certainly Bacterium germination come handle the new pollutant constantly synthesized be it is impossible, in conjunction with microorganism type, quantity and source, make its at For the core content of Sewage Biological Treatment.
The EMO compound bacteria microbial technique that the present invention uses has many advantages, such as follows compared with traditional activated sludge process: (1) A wide selection of colours and designs of microorganism, quantity are sufficient so that the decomposition of extremely complex intractable each type organic be able to it is smoothly complete At.(2) microbe species are more, adapt to toxic environment, and can share out the work and help one another, put out one's full powers, and complete challenge.(3) micro- life Object decomposing force extra-heavy, therefore can eliminate stink reduces amount of solid, and sludge is greatly reduced, thus can reduce processing cost with Operation difficulty.(4) decoloring ability traditional biological method victory matched compared with physical-chemical process exceedes 10 times.(5) processing capacity and achievement be Break the traditional concept of a lot of bioanalysis.EMO compound bacteria microbial technique and the comparison of traditional activated sludge process are as follows:
Traditional activated sludge process EMO compound bacteria microbial technique
It is big to add chemical drugs dosage, it is a lot of to generate sludge Without this problem
Overall cost of erection is quite big, and land occupation is wide, the device is complicated Without this problem
The removal rate of nitrogen (ammonia nitrogen) is relatively low Without this problem
Quantity, the type of microorganism be not complete, and CODcr removal rate is low Without this problem
When toxicant is more, the survival of microorganism is influenced Without this problem
The organic matter removal that hardly possible is decomposed is difficult Without this problem
A large amount of air must be supplied, energy source consumption is very big Without this problem
Often there is sludge extruding problem Without this problem
In the specific implementation, the decomposition chain that high definition microorganism is constituted.The decomposing force of various microorganisms be it is different, Selection high definition microbial species are implanted in sewage, and constitute the big feature that biological chain is EMO compound bacteria microbial technique.Its The microorganism of high definition abundant is achieved the biological treatment of the difficult biochemical waste water of certain BOD/COD < 0.3 in system, For high definition microorganism, the numerical value of the BOD of waste water is not conventional biochemical concept.
Contrast on effect of the present invention in the breakthrough of inhibiting substances concentration limit is as follows:
The present invention using EMO compound bacteria microbial technique to Environmental Protection in China circle generally believe can not biochemical treatment waste water It is researched and developed, the result shows that, such as nitrobenzene waste water, black liquid, high SO4 2-、Cl-Waste water, the pigment of content are useless Water, waste water from dyestuff, sauce waste water processed, pharmacy waste water, agricultural chemicals waste water, coking wastewater, gourmet powder waste water, saccharin wastewater etc. are completely may be used With what is handled using EMO compound bacteria microbial technique.
The compound bacteria microorganism of EMO in the present invention only need to be added once, without adding domestication and rejuvenation.Present invention incorporates Proprietary microbe carrier technique for fixing, proprietary microbe carrier increase the contact surface of microorganism and dirty organic pollutants Product, and certain buffer function can be played, while proprietary microbe carrier has certain specific gravity, it is ensured that microbial biomass fills Sufficient and proprietary microbe carrier is not lost.
As shown in Figure 1, a kind of method of the advanced treatment process of paraquat production waste water described in the present embodiment, implements Divide 5 stages: civil construction stage, proprietary bio-carrier add the stage, the compound bacteria microorganism of EMO adds the activation stage, domestication Stage, operation phase.It is specific as follows:
(1) it the civil construction stage: requires to build ABR and SBR biochemistry pool and other mating structures according to technique, and pacifies Tubulature road and equipment.
(2) proprietary bio-carrier adds the stage: requiring to add proprietary bio-carrier to ABR and SBR according to technique.
(3) the compound bacteria microorganism of EMO adds the activation stage: as requested respectively activate ABR and SBR microorganism, and to ABR and SBR are added.
(4) tame the stage: ABR fills it up with waste water in pond, plays self-loopa, and SBR is added portionwise waste water and is aerated.
(5) operation phase: after the completion of microbial acclimation, entire technique starts continuous operation, monitors each biochemistry pool daily Inlet and outlet water index.
Serial number Index Unit Influent quality Effluent quality
1 CODcr mg/L < 1500 ≤240
2 Ammonia nitrogen mg/L < 100 ≤5
3 Paraquat mg/L < 30 ≤1
4 pH 7-8 6-9
Continuous operation 1 month, the water outlet paraquat of biochemistry pool was almost monitored less than COD and ammonia nitrogen have also all reached discharge Standard illustrates EMO compound bacteria microbial technique to the efficient removal rate of paraquat production waste water.
It should be noted that paraquat production method for biologically treating wastewater disclosed by the invention can also be suitable for clethodim The processing of waste water, when handling clethodim waste water, influent quality is COD < 10000mg/L;Kjeldahl nitrogen < 400mg/L;After processing Effluent quality be COD≤500mg/L;Ammonia nitrogen≤35mg/L;
The present invention can also be suitable for the processing of Florfenicol waste water, and when handling Florfenicol waste water, influent quality is COD < 10000mg/L;Kjeldahl nitrogen < 400mg/L;Treated, and effluent quality is COD≤500mg/L;Ammonia nitrogen≤35mg/L.
The preferred embodiment for the present invention is explained in detail above in conjunction with attached drawing, but the present invention is not limited to above-mentioned implementations Mode within the knowledge of a person skilled in the art can also be without departing from the purpose of the present invention It makes a variety of changes, these variations are related to the relevant technologies well-known to those skilled in the art, these both fall within the invention patent Protection scope.
Many other changes and remodeling can be made by not departing from the spirit and scope of the present invention.It should be appreciated that the present invention is not It is limited to specific embodiment, the scope of the present invention is defined by the following claims.

Claims (4)

1. a kind of paraquat produces method for biologically treating wastewater, it is characterised in that: include 5 steps: the civil construction stage, proprietary Bio-carrier adds the stage, the compound bacteria microorganism of EMO adds activation stage, domestication stage, operation phase;Specific step is as follows:
(1) the civil construction stage: requiring to build ABR, SBR biochemistry pool and mating structures according to technique, and pipe laying and Equipment;
(2) proprietary bio-carrier adds the stage: requiring to add proprietary bio-carrier to ABR and SBR according to technique;
(3) the compound bacteria microorganism of EMO adds the activation stage: activate the microorganism of ABR and SBR respectively as requested, and to ABR and SBR is added;
(4) tame the stage: ABR fills it up with waste water in pond, plays self-loopa, and SBR is added portionwise waste water and is aerated;
(5) operation phase: after the completion of microbial acclimation, entire technique starts continuous operation, monitors the disengaging of each biochemistry pool daily Water index, until meeting processing requirement completes a process flow.
2. a kind of paraquat as described in claim 1 produces method for biologically treating wastewater, it is characterised in that: influent COD control Within 1500mg/L, the paraquat of water inlet is controlled within 30mg/L.
3. a kind of paraquat as claimed in claim 2 produces method for biologically treating wastewater, it is characterised in that: water outlet COD≤ 240mg/L, paraquat≤1mg/L have reached industrial wastewater discharge standard.
4. a kind of paraquat as described in claim 1 produces method for biologically treating wastewater, it is characterised in that: EMO compound bacteria is micro- Biology only need to be added once, without adding and rejuvenation;Bio-carrier only need to be added once.
CN201910660320.2A 2019-07-22 2019-07-22 A kind of paraquat production method for biologically treating wastewater Pending CN110342746A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910660320.2A CN110342746A (en) 2019-07-22 2019-07-22 A kind of paraquat production method for biologically treating wastewater

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910660320.2A CN110342746A (en) 2019-07-22 2019-07-22 A kind of paraquat production method for biologically treating wastewater

Publications (1)

Publication Number Publication Date
CN110342746A true CN110342746A (en) 2019-10-18

Family

ID=68179604

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910660320.2A Pending CN110342746A (en) 2019-07-22 2019-07-22 A kind of paraquat production method for biologically treating wastewater

Country Status (1)

Country Link
CN (1) CN110342746A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111875187A (en) * 2020-08-12 2020-11-03 湘潭建源生物技术开发有限公司 Biological treatment method for wastewater from indomethacin production
CN112723667A (en) * 2020-12-17 2021-04-30 重庆华歌生物化学有限公司 Method for treating high-salinity wastewater of sodium trichloropyridinol

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100475714C (en) * 2003-03-31 2009-04-08 科学与工业研究委员会 Sequential batch reactor with biofilm configuration for treating complex chemical and pharmaceutical effluent
CN101830602A (en) * 2010-05-18 2010-09-15 沈阳石蜡化工有限公司 Biochemical treatment method of acrylic ester industrial wastewater
KR20130091125A (en) * 2012-02-07 2013-08-16 인하대학교 산학협력단 Waste water treatment system by two stage anaerobic reactors coupled with nitrogen removal process
CN104556554A (en) * 2014-12-04 2015-04-29 江门谦信化工发展有限公司 Acrylic acid and ester wastewater deep treatment process method
CN108751597A (en) * 2018-06-22 2018-11-06 江苏宜裕环保科技有限公司 A kind of method of high-performance bio strain processing pyraclostrobin agricultural chemicals waste water

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100475714C (en) * 2003-03-31 2009-04-08 科学与工业研究委员会 Sequential batch reactor with biofilm configuration for treating complex chemical and pharmaceutical effluent
CN101830602A (en) * 2010-05-18 2010-09-15 沈阳石蜡化工有限公司 Biochemical treatment method of acrylic ester industrial wastewater
KR20130091125A (en) * 2012-02-07 2013-08-16 인하대학교 산학협력단 Waste water treatment system by two stage anaerobic reactors coupled with nitrogen removal process
CN104556554A (en) * 2014-12-04 2015-04-29 江门谦信化工发展有限公司 Acrylic acid and ester wastewater deep treatment process method
CN108751597A (en) * 2018-06-22 2018-11-06 江苏宜裕环保科技有限公司 A kind of method of high-performance bio strain processing pyraclostrobin agricultural chemicals waste water

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111875187A (en) * 2020-08-12 2020-11-03 湘潭建源生物技术开发有限公司 Biological treatment method for wastewater from indomethacin production
CN112723667A (en) * 2020-12-17 2021-04-30 重庆华歌生物化学有限公司 Method for treating high-salinity wastewater of sodium trichloropyridinol

Similar Documents

Publication Publication Date Title
Qin et al. Effects of exposure to polyether sulfone microplastic on the nitrifying process and microbial community structure in aerobic granular sludge
Guieysse et al. Sequential chemical–biological processes for the treatment of industrial wastewaters: review of recent progresses and critical assessment
CN101391851B (en) Treatment process of p toluidine-containing high concentration refractory organic wastewater
CN102452770A (en) Biochemical treatment/advanced oxidation treatment coupled sewage treatment technique
CN101376552A (en) Process for processing high concentration refractory organic wastewater containing paratoluidine
Babuponnusami et al. Advanced oxidation process (AOP) combined biological process for wastewater treatment: A review on advancements, feasibility and practicability of combined techniques
CN106477829B (en) Animal carcass harmless wastewater treatment system and wastewater treatment method
CN110342745A (en) A kind of macrolide antibiotics production method for biologically treating wastewater
CN101654314A (en) Dye waste water treatment method
CN101514070B (en) Disposal technique of nitrobenzene-containing sewage
CN108996808A (en) The biochemical combined treatment process and equipment of steel and iron industry concentrated water difficult to degrade
Lee et al. Pig slurry treatment by a hybrid multi-stage unit system consisting of an ATAD and an EGSB followed by a SBR reactor
Khalidi-Idrissi et al. Recent advances in the biological treatment of wastewater rich in emerging pollutants produced by pharmaceutical industrial discharges
Swain et al. Effect of mixing intensity on biodegradation of phenol in a moving bed biofilm reactor: Process optimization and external mass transfer study
CN110342746A (en) A kind of paraquat production method for biologically treating wastewater
CN110342744A (en) A kind of bioremediation of pyridine and its derivatives production waste water
Li et al. Effects of combined 4-chlorophenol and Cu2+ on functional genes for nitrogen and phosphorus removal and heavy metal resistance genes in sequencing batch bioreactors
Huang et al. Biological technologies for cHRPs and risk control
CN101704612A (en) Integrated treatment process of enhanced flocculation and bio-contact oxidation for high-salt oil-containing wastewater
Kuşçu et al. Treatment efficiencies of a sequential anaerobic baffled reactor (ABR)/completely stirred tank reactor (CSTR) system at increasing p-nitrophenol and COD loading rates
CN104909517A (en) Industrial production wastewater advanced treatment device
CN108609812A (en) A kind of method for processing organic wastewater
Zhou et al. Recent applications of biological technologies for decontaminating hormones in livestock waste and wastewater
CN108394983A (en) Salinity matrix is utilized to promote the method for Degradation of Antibiotics under a kind of high salt conditions in situ
Zhou et al. Improved integrated anaerobic–anoxic–oxic system for landfill leachate treatment using domestic wastewater as carbon source: Performance study and optimization

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
WD01 Invention patent application deemed withdrawn after publication
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20191018