WO2010083627A1 - 一种用于同步产电脱盐的污水处理工艺及装置 - Google Patents

一种用于同步产电脱盐的污水处理工艺及装置 Download PDF

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Publication number
WO2010083627A1
WO2010083627A1 PCT/CN2009/000111 CN2009000111W WO2010083627A1 WO 2010083627 A1 WO2010083627 A1 WO 2010083627A1 CN 2009000111 W CN2009000111 W CN 2009000111W WO 2010083627 A1 WO2010083627 A1 WO 2010083627A1
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anode
chamber
cathode
sewage treatment
desalination
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PCT/CN2009/000111
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English (en)
French (fr)
Inventor
黄霞
曹效鑫
梁鹏
肖康
周颖君
罗甘·布鲁斯
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清华大学
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Application filed by 清华大学 filed Critical 清华大学
Priority to AU2009338081A priority Critical patent/AU2009338081B2/en
Priority to US13/145,987 priority patent/US20110281139A1/en
Priority to PCT/CN2009/000111 priority patent/WO2010083627A1/zh
Priority to EP09838594.1A priority patent/EP2390236B1/en
Publication of WO2010083627A1 publication Critical patent/WO2010083627A1/zh

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    • 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
    • C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/469—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/42—Electrodialysis; Electro-osmosis ; Electro-ultrafiltration; Membrane capacitive deionization
    • B01D61/44—Ion-selective electrodialysis
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/42—Electrodialysis; Electro-osmosis ; Electro-ultrafiltration; Membrane capacitive deionization
    • B01D61/44—Ion-selective electrodialysis
    • B01D61/46—Apparatus therefor
    • B01D61/463—Apparatus therefor comprising the membrane sequence AC or CA, where C is a cation exchange membrane
    • 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
    • C02F3/005—Combined electrochemical biological processes
    • 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
    • C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/469—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
    • C02F1/4693—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis electrodialysis
    • 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
    • Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00—Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124—Water desalination

Definitions

  • the invention belongs to the technical field of water resources treatment, and particularly relates to a sewage treatment process and device for synchronous electric production desalination. Background technique ,
  • Water is an important natural resource for human survival.
  • the deterioration of the global water environment and the severe energy crisis urgently require efficient and low-cost wastewater resource technology to alleviate 'water shortages and energy demand.
  • 97% of the total water reserves on the earth are salt water (including seawater and brackish water).
  • Requiring fresh water to the sea and the lagoon to alleviate the growing global water crisis has not only reached a consensus in the global scientific community, but has also become The governments of the coastal countries advocate and develop countermeasures for new water sources.
  • seawater desalination has spread to 125 countries and regions around the world.
  • Desalination water feeds about 5% of the world's population.
  • Distillation, electrodialysis, ultrafiltration-reverse osmosis are the main desalination processes. These processes are highly efficient. But what comes with it is the high power consumption.
  • Microbial foel cell is a new wastewater treatment technology developed in recent years. It consists of an anode, a separator and a cathode. Its basic principle is to remove it by anodizing under the action of electrogenic microorganisms. Contaminants convert their chemical energy into electrical energy and produce electricity while treating sewage. From 2002 to the present, MFC output power has increased by nearly 10,000 times, initially showing bright and attractive application prospects.
  • the conventional MFC research idea is to use the current of the external circuit, but there is an internal current of the same size in the internal circuit. Referring to the principle of electrodialysis, we replace the internal single cation exchange membrane with two sets of membranes of cation and anion to form the intermediate cavity. In the chamber, if brine is added to the intermediate chamber, the internal current of the MFC can be used to desalinate while treating the sewage and producing electricity, thereby achieving three-in-one. Summary of the invention
  • the invention is based on microbial fuel cell technology and aims to simultaneously utilize the MFC to treat sewage, electricity and desalination processes.
  • the invention provides a sewage treatment process for synchronous electric desalination, characterized in that it comprises the following steps:
  • the sewage is a biodegradable organic wastewater.
  • the types of the electrogenic microorganisms include geobacter and shewanella.
  • the brine includes: seawater or brackish water, and the salt content is 5-35 g L.
  • the electron acceptor includes chemically catalytically reduced oxygen, potassium ferricyanide, and microbial catalytically reduced oxygen, nitrate, and carbon dioxide.
  • the present invention also provides a sewage treatment apparatus for synchronous generation of electric desalination, characterized in that the negative membrane 2 and the anode membrane 3 divide the microbial fuel cell 1 into an anode chamber A, an intermediate desalting chamber B and a cathode chamber C; An anode 4 is disposed in the anode chamber A, a cathode 5 is disposed in the cathode chamber C, and an electrogenic microbial membrane 6 is disposed on the anode 4.
  • the negative film 2 and the positive film 3 are non-toxic industrial electrodialysis ion exchange membranes having a transmittance of not less than 90%, a thickness of 0.2 to 0.5 mm, and a bursting strength of not less than 0.3 MPa.
  • the thickness of the electrogenic microorganism film 6 on the anode 4 is 20 to 80 ⁇ m.
  • the anode chamber inner anode 4 and the filling material include: graphite particles or carbon felt, and the particle size ranges from 1 to 5 mm P
  • the cathode 5 and the filling material in the cathode chamber C include: graphite particles or carbon felt, and the particle size ranges from 1 to 5 mm.
  • the invention has the beneficial effects that: the internal current of the microbial fuel cell (MFC) is desalted while treating the sewage and generating electricity, thereby achieving three-in-one; the process of the invention is simple, easy to operate, low in energy consumption and high in efficiency; The device has a simple structure and is convenient for industrial production and use.
  • MFC microbial fuel cell
  • FIG. 1 is a schematic view showing the principle of the desalted microbial fuel cell of the present invention.
  • the present invention provides a sewage treatment process and apparatus for simultaneous generation of electric desalination, and the present invention will be further described below in conjunction with the accompanying drawings and specific embodiments.
  • the anion membrane 2 and the anode membrane 3 divide the microbial fuel cell 1 into an anode chamber A, an intermediate desalting chamber B, and a cathode chamber C, wherein the anion membrane 2 and the anode membrane 3 are non-toxic industrial electricity having a transmittance of 95%.
  • the dialysis ion exchange membrane has a thickness of 0.3 mm and a bursting strength of 0.5 MPa; an anode 4 is disposed in the anode chamber A, a cathode 5 is disposed in the cathode chamber C, and an electrogenic microbial membrane 6 having a thickness of 40 ⁇ m is disposed on the anode 4,
  • the electrogenic microorganism uses geobacter, wherein the anode 4, the cathode 5, and the filling materials in the anode chamber A and the cathode chamber B are all carbon felts, the particle size ranges from 1 to 5 mm, and the filling materials in the anode chamber A and the cathode chamber B It is possible to increase the adhesion area and cathode area of the electrogenic microorganisms and increase the current.
  • the anode chamber A maintains an anaerobic state, and the biodegradable organic wastewater enters the anode chamber A, and oxidizes and removes pollutants in the sewage under the action of the electricity-producing microorganisms, and the electron-generating microorganisms transfer the electrons of the respiratory chain to the anode. 4.
  • the current direction of the external circuit flows from the cathode 5 to the anode 4; the current direction of the internal circuit flows from the anode 4 to the cathode 5, and the seawater having a salt content of 20 g/L continuously flows into the intermediate desalting chamber B, due to the negative membrane 2 and the anode membrane 3
  • the MFC output power is about 300W/m 3
  • the sewage treatment load is 5kg/m 3 d
  • the operating current is about 100 mA
  • the corresponding desalination rate is 90 mM/d.

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Water Supply & Treatment (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Health & Medical Sciences (AREA)
  • Molecular Biology (AREA)
  • Urology & Nephrology (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Organic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Description

一种用于同步产电脱盐的污水处理工艺及装置 技术领域
本发明属于水资源处理技术领域，特别涉及一种用于同步产电脱盐的污水处 理工艺及装置。 背景技术 ，
水是人类赖以生存的重要自然资源。 全球水环境的恶化和严重的能源危机， 迫切要求高效低耗的污水资源化技术， 以缓解 '水资源的短缺和对能源的需求。地 球上水的总储量中 97%是咸水 (包括海水和苦咸水)， 向大海和盐水湖索取淡水, 缓解日趋严重的世界性水危机,不仅已在全球科技界形成共识,也已成为各临海国 家的政府主张与开发新水源的对策。 目前海水淡化已遍及全世界 125个国家和地 区， 淡化水大约养活世界 5%的人口， 其中蒸馏法、 电渗析、 超滤-反渗透等是目 前主要的淡化工艺， 这些工艺处理效率很高， 但是随之而来的就是高额的电耗。
微生物燃料电池 （Microbial foel cell,简称 MFC) 是近年来发展起来的污水 处理新技术， 由阳极、 分隔膜和阴极三部分组成， 它的基本原理是以产电微生物 的作用下， 在阳极氧化去除污染物， 将其化学能转化为电能， 在处理污水的同时 产电。 从 2002年到现在， MFC输出功率提高了近万倍， 初步显示出光明、 诱人 的应用前景。 常规的 MFC研究思路是利用外电路的电流， 但是在内电路， 存在 相同大小的内电流； 借鉴电渗析的原理， 我们将内部的单一阳离子交换膜替换为 阳离子和阴离子两套膜，形成中间腔室，在中间腔室加入盐水，则可以利用 MFC 的内电流在处理污水、 产电的同时脱盐， 实现三效合一。 发明内容
本发明以微生物燃料电池技术为基础， 目的在于利用 MFC同时实现处理污 水， 产电以及脱盐过程。 本发明提供了一种用于同步产电脱盐的污水处理工艺， 其特征在于， 包括以下步骤：
(a)安装设备； (b)污水进入阳极室 A， 在产电微生物的作用下氧化去除污水中的污染物， 产电微生物将呼吸链的电子传递到阳极 4， 外电路电流方向为从阴极 5流向阳极 4;
(c)内电路电流方向为从阳极 4流向阴极 5，含盐水连续流入中间脱盐室 B, 由于阴膜 2和阳膜 3的选择性， 阴离子和阳离子在电驱动力作用下， 分别穿过阴 膜 2和阳膜 3到达阳极室 A和阴极室 C， 实现脱盐过程；
(d) 外电路的电子到达阴极 5与电子受体结合， 发生还原反应， 完成产电 过程。
所述污水为可生化处理的有机废水。
所述产电微生物的种类包括 geobacter和 shewanella。
所述含盐水包括： 海水或苦咸水， 含盐量为 5-35 g L。
所述电子受体包括化学催化还原的氧气、铁氰化钾以及微生物催化还原的氧 气、 硝酸盐、 二氧化碳。
本发明还提供了一种用于同步产电脱盐的污水处理装置， 其特征在于， 阴膜 2和阳膜 3将微生物燃料电池 1分为阳极室 A、 中间脱盐室 B和阴极室 C; 在阳 极室 A内设置阳极 4， 在阴极室 C内设置阴极 5, 并在阳极 4上布置产电微生物 膜 6。
所述阴膜 2和阳膜 3为透过率不小于 90%的无毒的工业用电渗析离子交换 膜， 厚度为 0.2〜0.5mm， 爆破强度不小于 0.3MPa。
所述阳极 4上的产电微生物膜 6的厚度为 20〜80μηι。
所述阳极室 Α内阳极 4及填充材料包括： 石墨颗粒或碳毡， 粒径范围为 1-5 mmP
所述阴极室 C内阴极 5及填充材料包括： 石墨颗粒或碳毡， 粒径范围为 1-5 mm。
本发明的有益效果为： 利用微生物燃料电池 （MFC) 的内电流在处理污水、 产电的同时脱盐， 实现三效合一； 本发明所述工艺简单， 易操作， 能耗低且效率 高； 所述装置结构简单， 便于工业生产及使用。 附图说明
图 1为本发明所述脱盐微生物燃料电池的原理示意图。
图中标号：
1-微生物燃料电池； 2-阴膜； 3-阳膜； 4-阳极； 5-阴极； 6-产电微生物膜。 具体实施方式
本发明提供了一种用于同步产电脱盐的污水处理工艺及装置， 下面结合附图 说明和具体实施方式对本发明做进一步说明。
图 1为本发明所述脱盐微生物燃料电池的原理示意图。 阴膜 2和阳膜 3将微 生物燃料电池 1分为阳极室 A、 中间脱盐室 B和阴极室 C， 其中， 阴膜 2和阳膜 3采用透过率为 95%的无毒的工业用电渗析离子交换膜， 厚度为 0.3mm， 爆破强 度为 0.5MPa; 在阳极室 A内设置阳极 4， 在阴极室 C内设置阴极 5， 并在阳极 4 上布置厚度为 40μπι的产电微生物膜 6， 产电微生物使用 geobacter, 其中， 阳极 4、阴极 5以及阳极室 A和阴极室 B内的填充材料均为碳毡，粒径范围为 1-5 mm, 阳极室 A和阴极室 B内的填充材料可以增大产电微生物的附着面积和阴极面积, 提高电流。
安装完成设备后， 阳极室 A保持厌氧状态，可生化处理的有机废水进入阳极 室 A， 在产电微生物的作用下氧化去除污水中的污染物， 产电微生物将呼吸链的 电子传递到阳极 4， 外电路电流方向为从阴极 5流向阳极 4; 内电路电流方向为 从阳极 4流向阴极 5，含盐量为 20g/L的海水连续流入中间脱盐室 B， 由于阴膜 2 和阳膜 3的选择性， 阴离子和阳离子在电驱动力作用下， 分别穿过阴膜 2和阳膜 3到达阳极室 A和阴极室( ， 实现脱盐过程； 外电路的电子到达阴极 5与电子受 体结合， 发生还原反应， 完成产电过程。
目前此 MFC输出功率约为 300W/m3， 污水处理负荷 5kg/m3d， 运行电流约 100 mA, 对应的脱盐速率为 90 mM/d， 随着 MFC技术的进步， 电流的增加将不 断的提高脱盐速率。

Claims

权 利 要 求 书
1. 一种用于同步产电脱盐的污水处理工艺， 其特征在于， 包括以下步骤：
(a) 安装设备；
(b)污水进入阳极室 （A)， 在产电微生物的作用下氧化去除污水中的污染 物， 产电微生物将呼吸链的电子传递到阳极（4)， 外电路电流方向为从阴极（5 ) 流向阳极 (4) ;
(c) 内电路电流方向为从阳极（4)流向阴极（5)， 含盐水连续流入中间脱 盐室（B)， 由于阴膜（2)和阳膜（3 ) 的选择性， 阴离子和阳离子在电驱动力作 用下， 分别穿过阴膜 （2)和阳膜（3 ) 到达阳极室 （A)和阴极室 （C)， 实现脱 盐过程；
(d)外电路的电子到达阴极（5 )与电子受体结合， 发生还原反应， 完成产 电过程。
2. 根据权利要求 1所述的一种用于同步产电脱盐的污水处理工艺， 其特征 在于， 所述污水为可生化处理的有机废水。
3. 根据权利要求 1所述的一种用于同步产电脱盐的污水处理工艺， 其特征 在于， 所述产电微生物的种类包括 geobacter和 shewanelk。
4. 根据权利要求 1所述的一种用于同步产电脱盐的污水处理工艺， 其特征 在于， 所述含盐水包括： 海水或苦咸水， 含盐量为 5-35 g/L。
5. 根据权利要求 1所述的一种用于同步产电脱盐的污水处理工艺， 其特征 在于， 所述电子受体包括化学催化还原的氧气、 铁氰化钾以及微生物催化还原的 氧气、 硝酸盐、 二氧化碳。
6. 一种用于同步产电脱盐的污水处理装置， 其特征在于， 阴膜（2)和阳膜 (3 )将微生物燃料电池（1 )分为阳极室（A)、 中间脱盐室（B)和阴极室（C) ; 在阳极室（A) 内设置阳极（4)， 在阴极室（C) 内设置阴极（5)， 并在阳极（4) 上布置产电微生物膜 （6)。
7. 根据权利要求 6所述的一种用于同步产电脱盐的污水处理装置， 其特征 在于， 所述阴膜（2)和阳膜（3 )为透过率不小于 90%的无毒的工业用电渗析离 子交换膜， 厚度为 0.2〜0.5mm， 爆破强度不小于 0.3MPa。
8. 根据权利要求 6所述的一种用于同步产电脱盐的污水处理装置， 其特征 在于， 所述阳极 （4)上的产电微生物膜 （6) 的厚度为 20〜80μπι。
9. 根据权利要求 6所述的一种用于同步产电脱盐的污水处理装置， 其特征 在于， 所述阳极室（Α) 内阳极（4)及填充材料包括： 石墨颗粒或碳毡， 粒径范 围为 1-5 mm。
10. 根据权利要求 6所述的一种用于同步产电脱盐的污水处理装置， 其特征 在于， 所述阴极室（C) 内阴极（5 )及填充材料包括： 石墨颗粒或碳毡， 粒径范 围为 1-5 mm。
PCT/CN2009/000111 2009-01-23 2009-01-23 一种用于同步产电脱盐的污水处理工艺及装置 WO2010083627A1 (zh)

Priority Applications (4)

Application Number Priority Date Filing Date Title
AU2009338081A AU2009338081B2 (en) 2009-01-23 2009-01-23 Wastewater treatment process and device for electricity generation and desalination simultaneously
US13/145,987 US20110281139A1 (en) 2009-01-23 2009-01-23 Wastewater Treatment Process and Device for Electricity Generation and Desalination Simultaneously
PCT/CN2009/000111 WO2010083627A1 (zh) 2009-01-23 2009-01-23 一种用于同步产电脱盐的污水处理工艺及装置
EP09838594.1A EP2390236B1 (en) 2009-01-23 2009-01-23 Sewage treatment process and apparatus for generating electric current and desalting simultaneously

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PCT/CN2009/000111 WO2010083627A1 (zh) 2009-01-23 2009-01-23 一种用于同步产电脱盐的污水处理工艺及装置

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