CN106587527A - Treatment method of deaminized landfill leachate - Google Patents
Treatment method of deaminized landfill leachate Download PDFInfo
- Publication number
- CN106587527A CN106587527A CN201611259253.6A CN201611259253A CN106587527A CN 106587527 A CN106587527 A CN 106587527A CN 201611259253 A CN201611259253 A CN 201611259253A CN 106587527 A CN106587527 A CN 106587527A
- Authority
- CN
- China
- Prior art keywords
- waste water
- composite powder
- solid
- mnzn composite
- returned
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/70—Treatment of water, waste water, or sewage by reduction
- C02F1/705—Reduction by metals
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/105—Phosphorus compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/06—Contaminated groundwater or leachate
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
The invention provides a treatment method of deaminized landfill leachate. The treatment method comprises the processes of CO2 preneutralization, liquid-solid separation, manganese-zinc powder reduction through CO2 pressurization, anaerobic treatment, aerobiotic treatment, biologic filtering tower treatment and the like. Treated waste water can be stably discharged in an up-to-standard mode.
Description
Technical field
The present invention relates to a kind of processing method of the percolate Jing after deamination process.
Background technology
Garbage loading embeading inevitably produces percolate.Pollutants from landfill leachate COD concentration is high, and composition is multiple
Miscellaneous, intractability is big.If the waste water is not processed is directly discharged into environment, severe contamination will be caused to environment.Current percolate
The main method combined using biological treatment and materializing strategy is processed.It is a considerable amount of due to containing in percolate
Persistence organic pollutant(Containing phenyl ring and(Or)Heterocycle Organic substance), thereby resulting in Biochemical method percolate can not be up to standard
Discharge.Generally percolate first uses blow-off method deamination, then Jing biological treatments, eventually passes reverse osmosiss or advanced oxidation(Such as
Fenton methods, catalytic oxidation etc.)Further processing could qualified discharge.Reverse-osmosis treated can produce concentrated water, this part concentrated water
General recharge landfill waste, the salinity for thus causing percolate increases, reverse-osmosis treated is adversely affected, when serious
Reverse osmosis treatment system is caused to be paralysed.Advanced oxidation processes processing cost is high.Development cost is low, the rubbish of energy stably reaching standard discharge oozes
The processing method of filtrate has larger practical value.
The content of the invention
For the problem that current method for treating garbage percolation liquid is present, the purpose of the present invention is to find low cost, can stablize
The processing method of the percolate of qualified discharge, it is characterised in that by the percolate CO Jing after deamination process2(CO2Can
Being industrial CO2, or fuel combustion, the CO that mineral decompose, sweat is produced2)PH value is neutralized less than 7, liquid is carried out
Gu separating, the waste water isolated enters regulating reservoir, and the solid isolated returns refuse landfill landfill.After adjusted pond is adjusted
Waste water sends into voltage-resistant reactor, and cleaning MnZn composite powder is added into reactor, and is passed through industrial CO2Reacted, MnZn is combined
The granularity of powder is less than 180 mesh, and the content of every kind of metal is not less than 5% in MnZn composite powder(The MnZn composite powder that return is used is not received
This restriction), every liter of waste water adds MnZn composite powder 10g~40g, and the stirring reaction time is 1h~3h, and reaction temperature is 25 DEG C~
60 DEG C, CO2Pressure be 0.3MPa~1.0MPa.Reacted waste water carries out solid-liquor separation, and the MnZn composite powder isolated is returned
Return reactor.Waste water lime cream or other alkaline matters after solid-liquor separation adjusts its pH value to 7.0~8.5, subsequently into
Anaerobic reactor.Waste water stops 24h~120h in anaerobic reactor, and anaerobism temperature is 25 DEG C~55 DEG C.Waste water after anaerobism enters
Enter biology aerobic pond room temperature to process, the Aerobic Process for Treatment time is 6h~16h.Waste water after Aerobic Process for Treatment enters sedimentation tank, during precipitation
Between be 1h~3h.Irregularly extract sludge out from sedimentation tank to be filtered, filter cake returns refuse landfill landfill, filtrate returns
Oxygen pond.The supernatant waste water of sedimentation tank send multi-layer biological filter tower to process.The filler of biological filtering tower combined working is activated carbon or porous ceramic grain, per layer
Thickness is 0.5m~2.0m, and gross thickness is 2m~4m.The dominant bacteria of biological filtering tower combined working is the rhodopseudomonas in photosynthetic bacteria
(Rhodopseudomonas).The hydraulic load of biological filtering tower combined working is 40 m3/m2.d~100m3/m2.d.The water outlet of biological filtering tower combined working reaches
Mark discharge.
The object of the present invention is achieved like this, Jing deaminations process percolate solid matter it is more, basicity compared with
Height, if using adding lime cream to carry out stripping deamination technique, the percolate contains more Ca2+, it and CO2It is anti-in percolate
CaCO should be generated3.Before into MnZn composite powder reduction reactor, CO is used2Preneutralization precipitation is carried out, and carries out solid-liquor separation, kept away
Exempt from solid matter and generate CaCO3Impact to the reduction of MnZn composite powder, is also beneficial to the complete MnZn composite powder of unreacted and reclaims
Recycle.The waste water isolated is entered after MnZn composite powder reduction reactor, the larger molecular organicses in waste water, particularly persistently
Property organic pollution(Containing phenyl ring and(Or)The Organic substance of heterocycle etc.)The strong reduction free radical for producing is reduced by MnZn composite powder
Effect and destroy, be subsequent biochemical process create favorable conditions.It is passed through pressure CO2Purpose be to maintain the reduction of MnZn composite powder
Suitable pH value(2.0~5.0), the waste water lime cream or other alkaline matters after reduction adjusts its pH value, follow-up to meet
The requirement of anaerobic and aerobic process.In anaerobic processes, by the effect of microorganism, macromole is organic for the premenstrual waste water for stating process
Thing further becomes small organic molecule, is that more favorable condition is created in subsequent bio oxidation.It is remaining by biological oxidation process
Most of Organic substances are removed, while going to denitrogenate the pollutant such as phosphorus.Waste water finally enters activated carbon or porous ceramic grain biological filtering tower combined working,
In the presence of microorganism, particularly rhodopseudomonas, the pollutant such as further organics removal and nitrogen phosphorus, it is ensured that after process
Waste water stably reaching standard is discharged.
Relative to existing method, the outstanding advantages of the present invention are reduced using MnZn composite powder, by percolate
Persistence organic pollutant is destroyed, and is that subsequent biological treatment creates favorable conditions, so as to ensure the waste water stably reaching standard after processing
Discharge;Relative to the metal deoxidization used in other wastewater treatments, using CO2Now widely used sulphuric acid is replaced to make acid
Agent, does not introduce SO4 2-Ion, eliminates generation H2The material base of S, so as to avoid H2The pollution of S, while it also avoid
SO4 2-Inhibitory action to microorganism during anaerobic and aerobic, greatly improves the efficiency of biological treatment;Refuse landfill is filled
Containing abundant CO in waste gas2Waste gas is available for utilizing, and can not only reduce processing cost, and can reduce carbon emission;After process
Waste water energy stably reaching standard is discharged, with obvious economic benefit and environmental benefit.
Specific implementation method
Embodiment 1:1m is processed daily3Deamination percolate(Composition:CODCr45000 mg/L、NH3-N115 mg/L、T-
P30mg/L), Jing CO2Preneutralization, solid-liquor separation, the reduction of MnZn composite powder(1h、40℃、CO2Pressure 0.8MPa, every liter of waste water add
Enter MnZn composite powder 30g), anaerobism(PH8.5,96h, 25 DEG C~35 DEG C), it is aerobic(10h)And biological filtering tower combined working(Porous ceramic grain filler
Layer gross thickness 4m, hydraulic load 100m3/m2.d)The COD of water outlet after processCrFor 59mg/L, NH3-N 5.7mg/L、T-P0.4mg/
L。
Embodiment 2:5m is processed daily3Deamination percolate(Composition: CODCr18000 mg/L、NH3-N43 mg/L、
T-P13mg/L), Jing CO2Preneutralization, solid-liquor separation, the reduction of MnZn composite powder(2h、25℃、CO2Pressure 0.3MPa, every liter of waste water
Add MnZn composite powder 10g), anaerobism(PH7.0,24h, 35 DEG C~55 DEG C), it is aerobic(6h)And biological filtering tower combined working(Active carbon filler layer
Gross thickness 2m, hydraulic load 50m3/m2.d)The COD of water outlet after processCrFor 46mg/L, NH3-N4.4mg/L、T-P0.4mg/L。
Claims (1)
1. it is a kind of Jing deamination process after percolate processing method, it is characterised in that by Jing deamination process after rubbish
Percolate CO2PH value is neutralized less than 7, solid-liquor separation is carried out, the waste water isolated enters regulating reservoir, and the solid isolated is returned
Refuse landfill landfill is returned, the waste water after adjusted pond is adjusted sends into voltage-resistant reactor, and cleaning MnZn composite powder is added into reaction
Device, and it is passed through industrial CO2Reacted, the granularity of MnZn composite powder is less than 180 mesh, the content of every kind of metal in MnZn composite powder
It is not less than 5%, every liter of waste water adds MnZn composite powder 10g~40g, the stirring reaction time is 1h~3h, reaction temperature is 25 DEG C~
60 DEG C, CO2Pressure be 0.3MPa~1.0MPa, reacted waste water carries out solid-liquor separation, and the MnZn composite powder isolated is returned
Reactor is returned, the waste water lime cream or other alkaline matters after solid-liquor separation adjusts its pH value to 7.0~8.5, subsequently into
Anaerobic reactor, waste water stops 24h~120h in anaerobic reactor, and anaerobism temperature is 25 DEG C~55 DEG C, and the waste water after anaerobism enters
Enter biology aerobic pond room temperature to process, the Aerobic Process for Treatment time is 6h~16h, and the waste water after Aerobic Process for Treatment enters sedimentation tank, during precipitation
Between be 1h~3h, irregularly extract sludge out from sedimentation tank and filtered, filter cake returns refuse landfill landfill, and filtrate returns
Oxygen pond, the supernatant waste water of sedimentation tank send multi-layer biological filter tower to process, and the filler of biological filtering tower combined working is activated carbon or porous ceramic grain, filler
Gross thickness is 2m~4m, and the dominant bacteria of biological filtering tower combined working is the rhodopseudomonas in photosynthetic bacteria, the hydraulic load of biological filtering tower combined working
For 40 m3/m2.d~100m3/m2.d, the standard water discharge discharge of biological filtering tower combined working.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201611259253.6A CN106587527A (en) | 2016-12-30 | 2016-12-30 | Treatment method of deaminized landfill leachate |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201611259253.6A CN106587527A (en) | 2016-12-30 | 2016-12-30 | Treatment method of deaminized landfill leachate |
Publications (1)
Publication Number | Publication Date |
---|---|
CN106587527A true CN106587527A (en) | 2017-04-26 |
Family
ID=58582801
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201611259253.6A Pending CN106587527A (en) | 2016-12-30 | 2016-12-30 | Treatment method of deaminized landfill leachate |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN106587527A (en) |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101665311A (en) * | 2009-09-24 | 2010-03-10 | 中南大学 | Catalysis and micro-electrolysis combined technology for high-concentration refractory organic wastewater |
-
2016
- 2016-12-30 CN CN201611259253.6A patent/CN106587527A/en active Pending
Patent Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101665311A (en) * | 2009-09-24 | 2010-03-10 | 中南大学 | Catalysis and micro-electrolysis combined technology for high-concentration refractory organic wastewater |
Non-Patent Citations (5)
Title |
---|
宋志伟等: "《水污染控制工程》", 31 July 2013, 中国矿业大学出版社 * |
张修正: "《化工厂电气手册》", 31 December 1994, 化学工业出版社 * |
施悦等: "《环境氧化还原处理技术原理与应用》", 31 August 2013, 哈尔滨工业大学出版社 * |
湖南省爱国卫生运动委员会办公室: "《爱国卫生运动工作手册》", 31 July 1986, 湖南人民出版社出版 * |
郑西来: "《地下水污染控制》", 31 July 2009, 华中科技大学出版社 * |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN106673331A (en) | Method for treating landfill leachate after deamination treatment | |
CN106673329A (en) | Method for treating landfill leachate after deamination treatment | |
CN106698830A (en) | Treatment method of deaminized landfill leachate | |
CN106587527A (en) | Treatment method of deaminized landfill leachate | |
CN106517682A (en) | Method for treating landfill leachate after deamination treatment | |
CN106673330A (en) | Treatment method for deaminized landfill leachate | |
CN106673345A (en) | Treatment method of landfill leachate subjected to deamination treatment | |
CN106746320A (en) | The processing method of the percolate after deamination treatment | |
CN106746300A (en) | The processing method of the percolate after deamination treatment | |
CN106517688A (en) | Treatment method for landfill leachate obtained after deamination treatment | |
CN106673358A (en) | Treatment method of landfill leachate subjected to deamination treatment | |
CN106746318A (en) | The processing method of the percolate after deamination treatment | |
CN106746269A (en) | The processing method of the percolate after deamination treatment | |
CN106746319A (en) | The processing method of the percolate after deamination treatment | |
CN106746265A (en) | The processing method of the percolate after deamination treatment | |
CN107043193A (en) | The processing method of percolate after deamination processing | |
CN106746299A (en) | The processing method of the percolate after deamination treatment | |
CN106746270A (en) | The processing method of the percolate after deamination treatment | |
CN106698840A (en) | Treatment method of deaminated landfill leachate | |
CN106587525A (en) | Treatment method for landfill leachate obtained after deamination | |
CN106746301A (en) | The processing method of the percolate after deamination treatment | |
CN106587517A (en) | Deaminized landfill leachate treatment method | |
CN106698841A (en) | Treatment method of deaminized landfill leachate | |
CN106746268A (en) | The processing method of the percolate after deamination treatment | |
CN106673328A (en) | Treatment method of landfill leachate subjected to deamination treatment |
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 | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20170426 |
|
RJ01 | Rejection of invention patent application after publication |