CN103224313B - Sediment in-situ treatment device and method utilizing microbial fuel cell - Google Patents
Sediment in-situ treatment device and method utilizing microbial fuel cell Download PDFInfo
- Publication number
- CN103224313B CN103224313B CN201310150096.5A CN201310150096A CN103224313B CN 103224313 B CN103224313 B CN 103224313B CN 201310150096 A CN201310150096 A CN 201310150096A CN 103224313 B CN103224313 B CN 103224313B
- Authority
- CN
- China
- Prior art keywords
- bed mud
- stainless steel
- porous plate
- fuel cell
- electric energy
- 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.)
- Active
Links
Images
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/20—Sludge processing
Abstract
The invention relates to a sediment in-situ treatment device and a sediment in-situ treatment method utilizing a microbial fuel cell. The invention relates to sediment treatment device and method. With an existing sediment treatment technology, secondary pollution can easily be caused. The invention aims at solving the problem. The device comprises a cathode, an anode stainless steel porous plate, an actuator, an actuator, an actuator, a motor, an electric energy management and control system, an engine, and a stirrer. The sediment treatment method comprises the steps that: 1, the microbial fuel cell sediment in-situ treatment device is placed into a river or a lake; when voltage in the electric energy management and control system reaches 500mV, the engine is driven, and the stirrer starts to stir; when voltage in the electric energy management and control system is reduced to 100mV, the motor is driven, the stainless steel porous plate moves upwards, and operation is stopped; and 2, the step 1 is repeated until the anode stainless steel porous plate moves to the upper surface of the sediment. The device provided by the invention has the advantages of simple structure, low cost, and no secondary pollution. The invention belongs to the field of sludge treatment.
Description
Technical field
The present invention relates to a kind of device and method of processing bed mud.
Background technology
Existing lake or bed mud in river treatment technology (as Sediment Dredging) exist a lot of problems, and Sediment Dredging is often costly on the one hand, and the environment aftereffect of engineering also exists a lot of uncertainties on the other hand, and very easily causes the generation of secondary pollution.Microbiological fuel cell, by organic anaerobic degradation, is converted into electric energy by chemical energy, produces the clean energy in decontamination.This technology has obtained laboratory and has confirmed, and has been applied in ocean environment, and the electric energy of generation is used for driving radio temperature sensor.
Summary of the invention
The object of the invention is easily to cause in order to solve existing sludge handling technology the technical problem of secondary pollution, a kind of device and method that utilizes microbiological fuel cell in-situ treatment bed mud is provided.
Utilize the device of microbiological fuel cell in-situ treatment bed mud, described device comprises negative electrode, anode stainless steel porous plate, driver, driver, driver, electric motor, electric energy managing and control system, engine and agitator, agitator, electric energy managing and control system are connected by wire with engine, electric energy managing and control system is connected by wire with anode stainless steel porous plate, electric energy managing and control system is connected by wire with negative electrode, and anode stainless steel porous plate, driver, driver, driver are connected by connection cord with electric motor.
Utilize the method for microbiological fuel cell in-situ treatment bed mud as follows:
One, will utilize the device of microbiological fuel cell in-situ treatment bed mud to put into river or lake, anode stainless steel porous plate be arranged in bed mud, and negative electrode is positioned at undersurface aerobic region, connection line, and anode stainless steel porous plate is inoculated 7 days-20 days in bed mud;
Two, the voltage in electric energy managing and control system reaches 500mV, drive engine to make agitator start to stir, voltage in electric energy managing and control system is reduced to 100mV, and drivingmotor moves up anode stainless steel porous plate under the drive of driver, driver and driver, out of service;
Three, repeating step two to anode stainless steel porous plate moves to apart from bed mud upper surface, completes and utilizes microbiological fuel cell in-situ treatment bed mud.
The present invention utilizes organic substance in bed mud as electron donor, and airborne oxygen is as final electron acceptor(EA), produces electric energy when realizing in bed mud organic matter degradation.The present invention is by energy managing and control system store electrical energy and control the position of anode in bed mud, has improved organic removal efficiency in bed mud, and gained electric energy is for driving the agitator of cathode surface.Apparatus of the present invention can be according to bed mud in river or lake and depth of water design height, and is Portable movable treatment unit, simple structure, and cost is low, non-secondary pollution.
Accompanying drawing explanation
Fig. 1 is the device schematic diagram that the present invention utilizes microbiological fuel cell in-situ treatment bed mud.
Embodiment
Technical solution of the present invention is not limited to following cited embodiment, also comprises the arbitrary combination between each embodiment.
Embodiment one: present embodiment is described in conjunction with Fig. 1, present embodiment is utilized the device of microbiological fuel cell in-situ treatment bed mud, described device comprises negative electrode 1, anode stainless steel porous plate 2, driver 3-1, driver 3-2, driver 3-3, electric motor 4, electric energy managing and control system 5, engine 6 and agitator 7, agitator 7, electric energy managing and control system 5 is connected by wire with engine 6, electric energy managing and control system 5 is connected by wire with anode stainless steel porous plate 2, electric energy managing and control system 5 is connected by wire with negative electrode 1, anode stainless steel porous plate 2, driver 3-1, driver 3-2, driver 3-3 is connected by connection cord with electric motor 4.
Embodiment two: what present embodiment was different from embodiment one is that described negative electrode 1 is stainless steel porous plate or carbon-point.Other is identical with embodiment one.
Embodiment three: present embodiment is different from one of embodiment one or two is that hole on described stainless steel porous plate is circular hole or slot.Other is not identical with one of embodiment one or two.
Embodiment four: present embodiment is different from one of embodiment one to three is that hole on described anode stainless steel porous plate 2 is circular hole or slot.Other is identical with one of embodiment one to three.
Embodiment five: present embodiment utilizes the method for microbiological fuel cell in-situ treatment bed mud as follows:
One, will utilize the device of microbiological fuel cell in-situ treatment bed mud to put into river or lake, anode stainless steel porous plate 2 is arranged in bed mud (anode stainless steel porous plate 2 is 3cm apart from the distance of river bed or lakebed), negative electrode 1 is positioned at undersurface aerobic region, connection line, anode stainless steel porous plate 2 is inoculated 7 days-20 days in bed mud;
Two, the voltage in electric energy managing and control system 5 reaches 500mV, drive engine 6 to make agitator 7 start to stir, voltage in electric energy managing and control system 5 is reduced to 100mV, drivingmotor 4 makes anode stainless steel porous plate 2 3cm that moves up under the drive of driver 3-1, driver 3-2 and driver 3-3, out of service;
Three, repeating step two to anode stainless steel porous plate 2 moves to the place apart from bed mud upper surface 1cm-3cm, completes and utilizes microbiological fuel cell in-situ treatment bed mud.
Embodiment six: what present embodiment was different from embodiment five is that the stainless steel of anode described in step 1 porous plate 2 is inoculated 9 days-15 days in bed mud.Other is identical with embodiment five.
Adopt following experimental verification effect of the present invention:
Test one:
Utilize the method for microbiological fuel cell in-situ treatment bed mud as follows:
One, utilize the device of microbiological fuel cell in-situ treatment bed mud to put into diameter for 20cm, high in the cylindrical reactor of 40cm (material is resin glass), anode stainless steel porous plate 2 is arranged in bed mud, negative electrode 1 is positioned at the position of underwater 3cm, connection line, anode stainless steel porous plate 2 is inoculated 14 days in bed mud;
Two, in initial 14 days, the voltage in electric energy managing and control system 5 presents unsure state, voltage in electric energy managing and control system 5 is 600mV, drive engine 6 to make agitator 7 start to stir, voltage after 120 days in electric energy managing and control system 5 is 100mV, drivingmotor 4 makes anode stainless steel porous plate 2 3cm that moves up under the drive of driver 3-1, driver 3-2 and driver 3-3, out of service, complete and utilize microbiological fuel cell in-situ treatment bed mud.
In bed mud in this test, organic content is 50g/kg (dry weight), in 120 days of one-period, near bed mud getting anode stainless steel porous plate 2 in 0,30,60,120 day respectively, contrast with open-circuit condition (there is no closed circuit, be equivalent to common anaerobic reactor); Each time period organic removal rate is as follows:
Table 1
Claims (2)
1. utilize the method for microbiological fuel cell in-situ treatment bed mud, it is characterized in that utilizing the method for microbiological fuel cell in-situ treatment bed mud as follows:
One, by utilizing the device of microbiological fuel cell in-situ treatment bed mud, put into river or lake, the wherein said agitator (7) that utilizes the device of microbiological fuel cell in-situ treatment bed mud, electric energy managing and control system (5) is connected by wire with engine (6), electric energy managing and control system (5) is connected by wire with anode stainless steel porous plate (2), electric energy managing and control system (5) is connected by wire with negative electrode (1), anode stainless steel porous plate (2), driver (3-1), driver (3-2), driver (3-3) is connected by connection cord with electric motor (4), anode stainless steel porous plate (2) is arranged in bed mud, negative electrode (1) is positioned at undersurface aerobic region, connection line, anode stainless steel porous plate (2) is inoculated 7 days-20 days in bed mud,
Two, the voltage in electric energy managing and control system (5) reaches 500mV, drive engine (6) to make agitator (7) start to stir, voltage in electric energy managing and control system (5) is reduced to 100mV, drivingmotor (4) makes anode stainless steel porous plate (2) 3cm that moves up under the drive of driver (3-1), driver (3-2) and driver (3-3), out of service;
Three, repeating step two to anode stainless steel porous plate (2) moves to the place apart from bed mud upper surface 1cm-3cm, completes and utilizes microbiological fuel cell in-situ treatment bed mud.
2. utilize according to claim 1 the method for microbiological fuel cell in-situ treatment bed mud, it is characterized in that the stainless steel of anode described in step 1 porous plate (2) inoculates 9 days-15 days in bed mud.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201310150096.5A CN103224313B (en) | 2013-04-26 | 2013-04-26 | Sediment in-situ treatment device and method utilizing microbial fuel cell |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201310150096.5A CN103224313B (en) | 2013-04-26 | 2013-04-26 | Sediment in-situ treatment device and method utilizing microbial fuel cell |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN103224313A CN103224313A (en) | 2013-07-31 |
| CN103224313B true CN103224313B (en) | 2014-01-22 |
Family
ID=48834992
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201310150096.5A Active CN103224313B (en) | 2013-04-26 | 2013-04-26 | Sediment in-situ treatment device and method utilizing microbial fuel cell |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN103224313B (en) |
Families Citing this family (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104787900B (en) * | 2015-04-14 | 2016-11-02 | 东南大学 | What electrochemistry strengthened that water body and bed mud purify simultaneously automatically controls aerating system |
| CN111285575A (en) * | 2019-04-13 | 2020-06-16 | 广州益禄丰生态环保科技有限责任公司 | Method and equipment for repairing urban tidal river black and odorous bottom mud by using microbial fuel cell |
| CN110803843A (en) * | 2019-11-21 | 2020-02-18 | 同济大学浙江学院 | Device and method for jointly degrading organic matters in water body sediment by utilizing waste scrap iron and sediment microbial fuel cell |
| CN111606526A (en) * | 2020-05-22 | 2020-09-01 | 重庆大学 | Novel method for developing oil-based mud by treating shale gas through double-chamber microbial fuel cell |
| CN114380362A (en) * | 2022-02-16 | 2022-04-22 | 西安建筑科技大学 | Device and method for synchronously removing nitrogen and phosphorus and realizing energy production |
| CN116425298B (en) * | 2023-03-09 | 2023-09-19 | 福建省厦门环境监测中心站(九龙江流域生态环境监测中心) | Microbial fuel cell sewage treatment equipment |
Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101615685A (en) * | 2009-07-17 | 2009-12-30 | 广东省生态环境与土壤研究所 | A kind of sediment in-situ is cut down the method and the device of microorganism electricity generation simultaneously |
| CN201485836U (en) * | 2009-08-25 | 2010-05-26 | 安徽省环境科学研究院 | Anti-wave closed column lifting along with water-depth changes in situ biological treatment |
| CN101841053A (en) * | 2009-05-12 | 2010-09-22 | 中国科学院南京地理与湖泊研究所 | Microbiological fuel cell (MFC) and application thereof in removing organisms from natural sediments |
| CN101924227A (en) * | 2010-08-18 | 2010-12-22 | 江南大学 | Microbial fuel cell and application thereof |
| CN101962232A (en) * | 2010-10-26 | 2011-02-02 | 中国科学院南京地理与湖泊研究所 | Sediment microorganism electrochemical device and application thereof |
| WO2010143865A3 (en) * | 2009-06-12 | 2011-03-10 | 광주과학기술원 | Three electrode type of microbial fuel cell and a method for operating the same |
| CN102231440A (en) * | 2011-04-20 | 2011-11-02 | 哈尔滨佳泰达科技有限公司 | Water body sediment microbiological fuel cell generating set and cathode processing method thereof |
| KR20120128865A (en) * | 2011-05-18 | 2012-11-28 | 관동대학교산학협력단 | A single reactor microbial fuel cell using sediment |
-
2013
- 2013-04-26 CN CN201310150096.5A patent/CN103224313B/en active Active
Patent Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101841053A (en) * | 2009-05-12 | 2010-09-22 | 中国科学院南京地理与湖泊研究所 | Microbiological fuel cell (MFC) and application thereof in removing organisms from natural sediments |
| WO2010143865A3 (en) * | 2009-06-12 | 2011-03-10 | 광주과학기술원 | Three electrode type of microbial fuel cell and a method for operating the same |
| CN101615685A (en) * | 2009-07-17 | 2009-12-30 | 广东省生态环境与土壤研究所 | A kind of sediment in-situ is cut down the method and the device of microorganism electricity generation simultaneously |
| CN201485836U (en) * | 2009-08-25 | 2010-05-26 | 安徽省环境科学研究院 | Anti-wave closed column lifting along with water-depth changes in situ biological treatment |
| CN101924227A (en) * | 2010-08-18 | 2010-12-22 | 江南大学 | Microbial fuel cell and application thereof |
| CN101962232A (en) * | 2010-10-26 | 2011-02-02 | 中国科学院南京地理与湖泊研究所 | Sediment microorganism electrochemical device and application thereof |
| CN102231440A (en) * | 2011-04-20 | 2011-11-02 | 哈尔滨佳泰达科技有限公司 | Water body sediment microbiological fuel cell generating set and cathode processing method thereof |
| KR20120128865A (en) * | 2011-05-18 | 2012-11-28 | 관동대학교산학협력단 | A single reactor microbial fuel cell using sediment |
Non-Patent Citations (4)
| Title |
|---|
| 吴佳佳等.沉积物微生物燃料电池研究进展.《电源技术》.2011,第35卷(第8期), |
| 宋天顺等.沉积物微生物燃料电池修复水体沉积物修复水体沉积物.《现代化工》.2009,第29卷(第11期), |
| 沉积物微生物燃料电池修复水体沉积物修复水体沉积物;宋天顺等;《现代化工》;20091130;第29卷(第11期);第15-19页 * |
| 沉积物微生物燃料电池研究进展;吴佳佳等;《电源技术》;20110831;第35卷(第8期);第1005-1008页 * |
Also Published As
| Publication number | Publication date |
|---|---|
| CN103224313A (en) | 2013-07-31 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN103224313B (en) | Sediment in-situ treatment device and method utilizing microbial fuel cell | |
| Lovley | Powering microbes with electricity: direct electron transfer from electrodes to microbes | |
| CN104176836A (en) | Microorganism electrochemical device for in-situ remediation of polluted water and bottom mud and method for in-situ remediation of polluted water and bottom mud | |
| KR20160059438A (en) | Hybridization systme of new and renewable energy technologies on the basis of salinity gradient power generation | |
| Rajesh et al. | Controlling methanogenesis and improving power production of microbial fuel cell by lauric acid dosing | |
| CN104377378A (en) | Microbial electrochemical apparatus and method for restoring nitrate-polluted underground water | |
| CN104277970B (en) | The apparatus and method of a kind of electromagnetically induced electrogenesis bacteria distribution, growth and domestication | |
| CN101805056B (en) | Control method of solar automatic aeration system | |
| CN102745781A (en) | Method for carrying out in-situ remediation on underground water nitrate pollution by adopting iron fuel cell | |
| CN106153700B (en) | Seabed sediment layer biofuel cell sensor system for in-situ monitoring of organic pollutant degradation | |
| Köroğlu et al. | Microbial fuel cells for energy recovery from waste | |
| CN102424474B (en) | New method for acclimating active sludge resisting high chloride ion wastewater | |
| CN211125848U (en) | Sedimentary microbial fuel cell for sludge treatment | |
| CN111606526A (en) | Novel method for developing oil-based mud by treating shale gas through double-chamber microbial fuel cell | |
| CN104671863A (en) | Bioelectrochemistry auxiliary anaerobic composting device capable of improving putrescibility of dewatered sludge and startup operation method thereof | |
| CN202569987U (en) | Vacuum homogeneous mixer | |
| CN107673566A (en) | A kind of device and method for handling black and odorous water | |
| CN207002526U (en) | A kind of multi-functional organic waste biochemical degradation device for experimental teaching | |
| CN204079695U (en) | A kind of integral solar energy waste disposal plant | |
| CN205023941U (en) | River course ecological remediation device | |
| CN205221080U (en) | Electronic bamboo raft | |
| CN206806449U (en) | Microbiological fuel cell purifier | |
| CN210403914U (en) | Sedimentary microbial fuel cell capable of utilizing wind power | |
| CN110451631A (en) | A kind of method of enhanced biological electrochemical in-situ pollution waters restoration | |
| CN203602402U (en) | Minitype microorganism electrolytic tank |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant |