CN101409355B - A photosynthetic microbial fuel cell - Google Patents
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- Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02E60/30—Hydrogen technology
- Y02E60/50—Fuel cells
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Abstract
一种光合微生物燃料电池,属于微生物燃料电池技术领域。光合微生物燃料电池由阴极、阳极两个电极室构成,通过质子交换膜连接,每个电极室装入定量的阳极室和阴极室溶液,光合微生物吸附在阳极表面,降解有机废物及重金属废水,同时进行光合作用,释放出电子和质子。光合微生物将电子转移给阳极,质子通过质子交换膜进入阴极,与空气中的氧结合生成水。电极间的电子转移使电极间产生电压,为外部电路供能。其优点在于:无需添加电子转移介体,无需通过外部动力来提高阴极表面的氧气含量,阳极无需另外添加养料在培养光合微生物(藻类、光合细菌)的同时产生电能,电池结构简单。阳极加入废水既提高电能,利于光合微生物的生长繁殖,节约成本,又能解决部分污染,生产氢气和甲烷。
A photosynthetic microbial fuel cell belongs to the technical field of microbial fuel cells. The photosynthetic microbial fuel cell consists of two electrode chambers, the cathode and the anode, which are connected by a proton exchange membrane. Each electrode chamber is filled with a certain amount of solution in the anode chamber and the cathode chamber. Photosynthetic microorganisms are adsorbed on the surface of the anode to degrade organic waste and heavy metal wastewater. Photosynthesis, releasing electrons and protons. Photosynthetic microorganisms transfer electrons to the anode, protons enter the cathode through the proton exchange membrane, and combine with oxygen in the air to form water. The transfer of electrons between the electrodes generates a voltage between the electrodes, which powers the external circuit. Its advantages are: no need to add electron transfer mediators, no need to increase the oxygen content on the surface of the cathode through external power, no need to add additional nutrients to the anode to generate electricity while cultivating photosynthetic microorganisms (algae, photosynthetic bacteria), and the battery structure is simple. Adding wastewater to the anode not only increases the electric energy, but also benefits the growth and reproduction of photosynthetic microorganisms, saves costs, and can solve some pollution and produce hydrogen and methane.
Description
技术领域technical field
本发明属于微生物燃料电池技术领域,涉及一种可以处理重金属/有机物复合污染物废水同时获得电能,并培养收获光合微生物(藻类、光合细菌),且产生沼气、氢气的装置。The invention belongs to the technical field of microbial fuel cells, and relates to a device capable of processing heavy metal/organic complex pollutant wastewater while obtaining electric energy, cultivating and harvesting photosynthetic microorganisms (algae, photosynthetic bacteria), and generating methane and hydrogen.
背景技术Background technique
微生物燃料电池(Microbial Fuel Cell)是以微生物(Microbe)作为催化剂,将燃料如糖、有机酸等的化学能转化为电能的装置。这种装置具有双重功能,即一方面可以处理污水,另一方面还可以利用污水中的有害废物作为原料发电。Microbial Fuel Cell is a device that uses microorganisms (Microbe) as a catalyst to convert the chemical energy of fuels such as sugar and organic acids into electrical energy. This device has dual functions, that is, on the one hand, it can treat sewage, and on the other hand, it can also use the harmful waste in the sewage as a raw material to generate electricity.
由于微生物燃料电池的这种自身潜在的优点使人们对它的发展前景很是看好,但是要做为电源用于实际生产与生活还比较遥远。其主要原因是输出功率密度远远不能满足实际要求。目前质子交换膜燃料电池的功率密度可达3W/cm2,而生物燃料电池的功率密度还达不到1mW/cm2,可见两者差距之大。制约生物燃料电池输出功率密度的最大因素是电子传递过程。由于代谢产生的还原性物质被微生物的膜与外界隔离,从而导致微生物与电极之间的电子传递通道受阻。尽管电池中的微生物可以将电子直接传递至电极,但电子传递量和传递速率很低。这是由于微生物细胞含有不导电物质,因此电子难以从正常的微生物电子传递链透过细胞膜传递到电极,解决这一问题的主要方法是向阴极室中加入氧化还原分子作为电子转移介体,但这些介体通常是有毒化合物并且价格较高,如将这种燃料电池应用与实际的废水处理并不经济。Due to the potential advantages of microbial fuel cells, people are very optimistic about its development prospects, but it is still far away to be used as a power source for actual production and life. The main reason is that the output power density is far from meeting the actual requirements. At present, the power density of the proton exchange membrane fuel cell can reach 3W/cm 2 , while the power density of the biofuel cell has not yet reached 1mW/cm 2 , which shows the huge gap between the two. The biggest factor restricting the output power density of biofuel cells is the electron transfer process. Since the reducing substances produced by metabolism are isolated from the outside world by the membrane of microorganisms, the electron transfer channel between microorganisms and electrodes is blocked. Although the microbes in the battery can transfer electrons directly to the electrodes, the amount and rate of electron transfer is low. This is because microbial cells contain non-conductive substances, so it is difficult for electrons to pass through the cell membrane from the normal microbial electron transport chain to the electrode. The main method to solve this problem is to add redox molecules to the cathode chamber as electron transfer mediators, but These mediators are usually toxic compounds and are expensive, such that it is not economical to apply such fuel cells to actual wastewater treatment.
韩国科学技术研究院的金炳弘等人申请了专利“一种用于废水处理的使用废水和活性污泥的生物燃料电池”(ZL00810805.6),该发明使用废水和活性污泥中的电化学活性微生物氧化废水中所含的有机物。生物燃料电池包括仅次于生物燃料电池内部的分别含导电介体的阴极隔室和阳极隔室;安置在阳极隔室中的阳极;安置在阴极隔室中的阴极;和介于阴极隔室和阳极隔室之间用于分隔阳极隔室和阴极隔室的离子交换膜,其中的阳极隔室含有有机废水和活性污泥并在生物燃料电池的操作过程中维持厌氧条件。虽然该燃料电池不需要添加任何电子转移介体,但是为了维持阳极池的厌氧和阴极池的高溶解氧状态,需要不断的向阳极池通入氮气,向阴极池通入氧气,加大了电池的运行成本。Kim Byung-hong and others from the Korea Institute of Science and Technology applied for a patent "A biofuel cell using wastewater and activated sludge for wastewater treatment" (ZL00810805.6), which uses the electrochemical activity in wastewater and activated sludge Microorganisms oxidize organic matter contained in wastewater. A biofuel cell includes a cathode compartment and an anode compartment respectively containing a conductive mediator next to the interior of the biofuel cell; an anode placed in the anode compartment; a cathode placed in the cathode compartment; and an intervening cathode compartment An ion exchange membrane used to separate the anode compartment and the cathode compartment between the anode compartment containing organic wastewater and activated sludge and maintaining anaerobic conditions during the operation of the biofuel cell. Although the fuel cell does not need to add any electron transfer mediator, in order to maintain the anaerobic state of the anode cell and the high dissolved oxygen state of the cathode cell, it is necessary to continuously feed nitrogen into the anode cell and oxygen into the cathode cell, increasing the The running cost of the battery.
浙江大学刘宜胜等人申请了发明专利“微生物燃料电池”(200410066753.9),Liu Yisheng of Zhejiang University and others applied for the invention patent "Microbial Fuel Cell" (200410066753.9),
这种微生物燃料电池的箱体内分隔成阳极腔体和阴极隔板,隔板上有孔,孔上设置有氢离子选择膜,阳极腔体内有由葡萄糖、磷酸二氢钠和亚甲基蓝(介体)配置的溶液,阳极腔体上盖有密封盖,密封盖上固定有阳极石墨棒,阳极石墨棒的一端伸入阳极腔体内浸于溶液中,该端具有蜂窝状小孔,蜂窝状小孔中置有啤酒酵母菌及其培养基,阴极腔体内盛有由铁氰化钾和延胡索酸亚铁配置的溶液,在阴极腔体上盖有端盖,端盖上固定有阴极石墨棒,阴极石墨棒的一端伸入阴极腔体内浸于腔体的溶液中。The cabinet of this microbial fuel cell is divided into an anode cavity and a cathode separator. There are holes on the separator, and a hydrogen ion selective membrane is arranged on the hole. There are glucose, sodium dihydrogen phosphate and methylene blue (mediator) in the anode cavity. The configured solution, the anode cavity is covered with a sealing cover, and the anode graphite rod is fixed on the sealing cover. One end of the anode graphite rod extends into the anode cavity and is immersed in the solution. Beer yeast and its culture medium are placed, and the cathode cavity is filled with a solution composed of potassium ferricyanide and ferrous fumarate. The cathode cavity is covered with an end cover, and the cathode graphite rod is fixed on the end cover. One end extends into the cathode cavity and is immersed in the solution in the cavity.
上述两个专利的微生物燃料电池由阴极室和阳极室组成,阳极都由介体来传递电子。介体的价格非常昂贵,而且需要经常补充,相对于生物燃料电池提供的功率,添加介体所付出的成本极高。且很多氧化还原介体有毒,使其不能在从有机物中获得能量的开放环境中使用。因此有氧化还原介体的微生物燃料电池不适于用做一种简单的长期能源。且浙江大学专利所用的酵母菌的培养基需将阳极取出定时添加,操作不便,而且应用范围小。The microbial fuel cells of the above two patents are composed of a cathode chamber and an anode chamber, and the anodes all use mediators to transfer electrons. The mediator is very expensive and needs to be replenished frequently. Compared with the power provided by the biofuel cell, the cost of adding the mediator is extremely high. And many redox mediators are toxic, making them unusable in open environments where energy is obtained from organic matter. Therefore, microbial fuel cells with redox mediators are not suitable for use as a simple long-term energy source. And the culture medium of yeast used in the patent of Zhejiang University needs to take out the anode and add it regularly, which is inconvenient to operate and has a small application range.
除此而外,还有其他形式的微生物燃料电池报导,但总体上所采用的微生物都是利用有机物为底物传递电子,不能直接利用方便易得、供应充足的太阳能。In addition, there are other forms of microbial fuel cell reports, but the microorganisms adopted generally use organic matter to transfer electrons as substrates, and cannot directly utilize the convenient and easy-to-obtain and abundantly supplied solar energy.
发明内容Contents of the invention
本发明的目的在于解决现有微生物燃料电池所采用的微生物都是利用有机物为底物传递电子,不能直接利用方便易得、供应充足的太阳能的问题。利用光能微生物燃料电池可培养藻并收集电能;利用该装置,光合微生物生长繁殖的同时,处理生活和工业有机废物、重金属废水,且输出电能提高,利于藻类生长繁殖,还可生产沼气、氢气。这种光合微生物燃料电池既为人类增加了一种能源方向,又可解决有机物、重金属污染问题,同时收获藻类,生产沼气、氢气。The purpose of the present invention is to solve the problem that the microorganisms used in the existing microbial fuel cells all use organic substances as substrates to transfer electrons, and cannot directly use convenient, readily available and adequately supplied solar energy. The use of light energy microbial fuel cells can cultivate algae and collect electrical energy; using this device, photosynthetic microorganisms can grow and reproduce while processing domestic and industrial organic waste and heavy metal wastewater, and the output power can be increased, which is conducive to the growth and reproduction of algae, and can also produce biogas and hydrogen . This photosynthetic microbial fuel cell not only adds an energy direction for human beings, but also solves the pollution problems of organic matter and heavy metals, and at the same time harvests algae to produce biogas and hydrogen.
一种光合微生物燃料电池,包括阴极室10和阳极室9,阴极室10和阳极室9通过质子交换膜6连接,质子交换膜与两极室之间夹有真空垫5以保持密封。阴阳极室均带有通气口2、进料口7及取样口8,上部均开口暴露于空气中形成好氧状态。阳极室带有取气口1,收取H2、CH4。阳极室内的石墨电极11与阴极室内石墨电极12通过导线与外部负载电阻3连接。阴阳极室装入阴极缓冲液,阳极室装入阳极缓冲液及培养基。石墨电极预先放入培养皿中进行光合微生物富集,形成成熟生物膜后,将吸附光合微生物4,形成成熟生物膜的阳极插入阳极室。有机废物及重金属废水可由阳极室的进料口加入,铁氰化钾可由阴极进料口加入。A photosynthetic microbial fuel cell, comprising a
本发明提供的无电子转移介体光合微生物燃料电池,光合微生物吸附在阳极表面,进行光合作用生长繁殖,同时降解有机废物及重金属废水,释放出电子和质子。光合微生物将电子转移给阳极,再通过外电路传递到阴极,质子通过质子交换膜进入阴极,电子、质子与空气中的氧结合生成水。电极间的电子转移使电极间产生电压,为外部电路供能。阳极在光合微生物在降解有机废物及重金属废水时,产生氢气和甲烷,可收集使用。并可定期收获藻类。In the photosynthetic microbial fuel cell without an electron transfer mediator provided by the invention, the photosynthetic microorganisms are adsorbed on the surface of the anode, carry out photosynthetic growth and reproduction, degrade organic waste and heavy metal wastewater at the same time, and release electrons and protons. Photosynthetic microorganisms transfer electrons to the anode, and then transfer them to the cathode through an external circuit. The protons enter the cathode through the proton exchange membrane, and the electrons and protons combine with oxygen in the air to form water. The transfer of electrons between the electrodes generates a voltage between the electrodes, which powers the external circuit. The anode produces hydrogen and methane when photosynthetic microorganisms degrade organic waste and heavy metal wastewater, which can be collected and used. And algae can be harvested regularly.
阳极室接入的是可以进行光合作用的微生物4,如小球藻、螺旋藻、鱼腥藻以及光合细菌等等。这种微生物接入阳极,无需另外添加养料,其本身就可以维持一定的电池电压,本装置的电压为0.09-0.2V,随着阴极加入铁氰化钾的量,阳极板的面积、数量的不同,电压值有所不同。The anode chamber is connected with microorganisms 4 capable of photosynthesis, such as Chlorella, Spirulina, Anabaena, and photosynthetic bacteria. When this kind of microorganism is connected to the anode, it can maintain a certain battery voltage without adding additional nutrients. The voltage of this device is 0.09-0.2V. With the amount of potassium ferricyanide added to the cathode, the area and quantity of the anode plate will increase. Different, the voltage value is different.
光合微生物在阳极室进行光合作用繁殖生长,可定期收获光合微生物,如小球藻、螺旋藻、鱼腥藻等等。Photosynthetic microorganisms carry out photosynthetic reproduction and growth in the anode chamber, and photosynthetic microorganisms, such as chlorella, spirulina, anabaena, etc., can be harvested regularly.
阳极中的光合微生物进行光合作用和生长繁殖的同时,可处理有机废物及重金属废水,提高电能的输出,利于藻类的生长繁殖。While the photosynthetic microorganisms in the anode carry out photosynthesis and growth and reproduction, they can treat organic waste and heavy metal wastewater, increase the output of electric energy, and benefit the growth and reproduction of algae.
光合微生物在降解有机废水的同时可生产沼气、氢气,提高太阳能利用率。Photosynthetic microorganisms can produce biogas and hydrogen while degrading organic wastewater, and improve the utilization rate of solar energy.
质子交换膜使用前需要依次在30%H2O2、0.5mol/L H2SO4及去离子水中煮沸1h,然后保存在去离子水中备用。电极均为未抛光的高纯石墨电极,使用前用1.0mol/L的HCl浸泡去除杂质离子,使用后再用1.0mol/L的NaOH浸泡以除去其表面吸附的细胞。石墨电极处理后,置于小球藻培养器皿中进行藻的富集,以备用。Before use, the proton exchange membrane needs to be boiled in 30% H 2 O 2 , 0.5mol/L H 2 SO 4 and deionized water for 1 hour, and then stored in deionized water for later use. The electrodes are all unpolished high-purity graphite electrodes. Before use, soak them in 1.0mol/L HCl to remove impurity ions, and then soak them in 1.0mol/L NaOH to remove cells adsorbed on their surfaces. After the graphite electrode is treated, it is placed in a chlorella culture vessel for algae enrichment for future use.
阳极缓冲液和阴极缓冲液,及光合微生物培养基需121℃灭菌15分钟,备用。The anode buffer, cathode buffer, and photosynthetic microorganism culture medium need to be sterilized at 121°C for 15 minutes and set aside.
光合微生物生长温度在0-80℃之间,最佳的温度在25-30℃,可以直接利用太阳光,外光源光照强度0-106lux,最佳光照强度4.5×103-5×103lux。负载电阻为0-10MΩ,随着负载电阻的增加,电池电压逐渐增大,但增长速率逐渐放缓。但电池功率先增大后变小,在最佳负载电阻附近电池输出功率最大,本装置的最佳负载电阻在500-530Ω,见图2。The growth temperature of photosynthetic microorganisms is between 0-80°C, and the best temperature is 25-30°C, which can directly use sunlight. The light intensity of the external light source is 0-10 6 lux, and the best light intensity is 4.5×10 3 -5×10 3 lux. The load resistance is 0-10MΩ. As the load resistance increases, the battery voltage gradually increases, but the growth rate gradually slows down. However, the battery power first increases and then decreases, and the battery output power is the largest near the optimum load resistance. The optimum load resistance of this device is 500-530Ω, as shown in Figure 2.
光合微生物燃料电池发生如下的反应:Photosynthetic microbial fuel cells undergo the following reactions:
光合作用: Photosynthesis:
阳极: anode:
阴极:O2+4H++4e-→H2O (4)Cathode: O 2 +4H + +4e - →H 2 O (4)
光合微生物燃料电池产生的电压由两部分组成:一部分是光合微生物(微藻、光合细菌)进行光合作用光解H2O,在这个过程中产生的电子和质子传递至阴极(公式(2));另一部分是外细胞代谢光合作用产生的碳水化合物的过程中,细胞膜外累积的细胞色素失去电子给阳极(公式(3)),电子再通过外电路到达阴极。质子通过质子交换膜传到阴极,电子由外电路传递至阴极,与水中的氧生成水(公式(4)),加入铁氰化钾加速电子的传递,有利于提高电压。The voltage generated by the photosynthetic microbial fuel cell is composed of two parts: one part is photosynthetic microorganisms (microalgae, photosynthetic bacteria) for photosynthetic photolysis of H 2 O, and the electrons and protons generated in this process are transferred to the cathode (formula (2)) The other part is the process of exogenous cell metabolism of carbohydrates produced by photosynthesis, the cytochrome accumulated outside the cell membrane loses electrons to the anode (formula (3)), and the electrons reach the cathode through the external circuit. The protons are transferred to the cathode through the proton exchange membrane, and the electrons are transferred to the cathode by the external circuit, and form water with the oxygen in the water (formula (4)). The addition of potassium ferricyanide accelerates the transfer of electrons, which is beneficial to increase the voltage.
本光合微生物燃料电池其优点在于:无需添加电子转移介体,无需通过外部动力来提高阳极表明微生物的燃料浓度,及阴极表面的氧气含量,且阳极无需另外添加养料以维持电池电压,电池结构简单。可利用微生物进行光合作用生长繁殖过程的能量降解有机废物及重金属废水,提高电能的同时,可生产沼、氢气。既利用光能养殖光合微生物的同时,可处理有机废物及重金属废物,获得电能,生产沼气、氢气。The advantages of the photosynthetic microbial fuel cell are: no need to add electron transfer mediators, no need to use external power to increase the fuel concentration of the anode surface microorganisms, and the oxygen content on the surface of the cathode, and the anode does not need to add additional nutrients to maintain the battery voltage, the battery structure is simple . Microorganisms can be used to degrade organic waste and heavy metal wastewater by using the energy of photosynthetic growth and reproduction process, and can produce biogas and hydrogen while increasing electric energy. While using light energy to cultivate photosynthetic microorganisms, it can also process organic waste and heavy metal waste, obtain electricity, and produce biogas and hydrogen.
附图说明Description of drawings
图1为光合微生物燃料电池结构示意图。Figure 1 is a schematic diagram of the structure of a photosynthetic microbial fuel cell.
1.取气口(H2、CH4);2.通气口(空气/O2);3.负载电阻;4.光合微生物;5.真空垫;6.质子交换膜;7.进料口;8.取料口;9.阳极室;10.阴极室;11.阳极石墨电极;12.阴极石墨电极1. Air intake (H 2 , CH 4 ); 2. Vent (air/O 2 ); 3. Load resistance; 4. Photosynthetic microorganisms; 5. Vacuum pad; 6. Proton exchange membrane; 7. Feed port; 8. Feed port; 9. Anode chamber; 10. Cathode chamber; 11. Anode graphite electrode; 12. Cathode graphite electrode
图2为电池的电阻-输出功率及电阻-电压图Figure 2 is the resistance-output power and resistance-voltage diagram of the battery
图3为小球藻微生物燃料电池的电压-时间曲线Figure 3 is the voltage-time curve of the chlorella microbial fuel cell
图4为光合细菌微生物燃料电池的电压-时间曲线(阳极加入生活废水)Figure 4 is the voltage-time curve of the photosynthetic bacteria microbial fuel cell (the anode is added to domestic wastewater)
图5为螺旋藻微生物燃料电池的电压-时间曲线(阳极加入某矿山有机废物-重金属复合废水)Figure 5 is the voltage-time curve of the spirulina microbial fuel cell (the anode is added to a mine organic waste-heavy metal composite wastewater)
具体实施方式Detailed ways
实施例一:Embodiment one:
微生物采用小球藻(Chlorella vulgaris),由河道取得的水样进行培养,利用水滴分离法分离所得。培养基成分(1L)如下表:The microorganisms are Chlorella vulgaris, cultured from water samples obtained from the river, and separated by the water droplet separation method. The medium composition (1L) is as follows:
表1培养基配方表(1L)Table 1 Medium formula table (1L)
表2培养基微量元素配方表(1L)Table 2 Medium trace element formula table (1L)
光合微生物燃料电池由阴极、阳极两个电极室构成,通过质子交换膜(Nation-117,Dupont)连接,质子交换膜与两极室之间夹有真空垫以保持密封,每个电极室可装入1000ml溶液,阳极板物理表面积75cm2,阳极室加入阳极缓冲液(表3)及上述的培养基,阴极室加入阴极缓冲液(表4)及铁氰化钾溶液。所有装置均置于光照培养箱中进行实验。生长温度在25-30℃,光照强度4.5×103lx,负载电阻确定为510Ω。The photosynthetic microbial fuel cell consists of two electrode chambers, the cathode and the anode, which are connected by a proton exchange membrane (Nation-117, Dupont). 1000ml solution, the physical surface area of the anode plate is 75cm 2 , add the anode buffer solution (Table 3) and the above-mentioned culture medium to the anode chamber, and add the cathode buffer solution (Table 4) and potassium ferricyanide solution to the cathode chamber. All devices were placed in a light incubator for experiments. The growth temperature is 25-30°C, the light intensity is 4.5×10 3 lx, and the load resistance is determined to be 510Ω.
表3阳极室缓冲液组成(/L)Table 3 Anode chamber buffer composition (/L)
表4阴极室缓冲液组成(/L)Table 4 Cathode chamber buffer composition (/L)
电极预先放入培养皿中进行小球藻富集,形成成熟生物膜后,将阳极插入极室时,电压迅速上升到0.2V左右,见图3。当铁氰化钾消耗完后,电池电压下降至0.12V,且稳定运行。将电极更换为未接入小球藻的电极,电压立即降至背景电压,再次更换为原始电极时,电压迅速上升到0.12V左右。表明电能的输出小球藻,既光合微生物起决定性的作用。阴极再加入50mmol/L铁氰化钾溶液,电压值迅速上升到0.2V。这是由于铁氰化钾中Fe3+的还原速率比O2氧化Fe2+的氧化速率快,可加速电子的传递速率,提高电能的输出。反应一段时间后,铁氰化钾消耗完,电池电压值下降趋于稳定。此时,注入50mmol/L铁氰化钾溶液,电压值迅速上升。7天后即可从阳极收获小球藻5.1克。The electrode is pre-placed in a petri dish for enrichment of chlorella. After forming a mature biofilm, when the anode is inserted into the electrode chamber, the voltage rises rapidly to about 0.2V, as shown in Figure 3. When the potassium ferricyanide is consumed, the battery voltage drops to 0.12V, and it operates stably. When the electrode is replaced with an electrode that is not connected to chlorella, the voltage immediately drops to the background voltage, and when the original electrode is replaced again, the voltage rises rapidly to about 0.12V. Show that the output of electrical energy Chlorella, both photosynthetic microorganisms play a decisive role. Then add 50mmol/L potassium ferricyanide solution to the cathode, and the voltage value rises rapidly to 0.2V. This is because the reduction rate of Fe 3+ in potassium ferricyanide is faster than the oxidation rate of Fe 2+ oxidized by O 2 , which can accelerate the transfer rate of electrons and increase the output of electric energy. After a period of reaction, the potassium ferricyanide is consumed, and the battery voltage drops and tends to be stable. At this time, inject 50mmol/L potassium ferricyanide solution, and the voltage value rises rapidly. After 7 days, 5.1 grams of Chlorella can be harvested from the anode.
实施例2:Example 2:
光合细菌(photosynthetic bacteria简称PSB)分离于北京小月河,分离用培养基为:有机物1.5-2g,(NH4)2SO4 1g,NaCl 2g,NaCO3 5g,K2HPO4 0.5g,MgSO4·7H2O0.2g,蒸馏水1000mL,pH 7.0,,温度25-30℃光照培养。分离出的PSB成革兰氏阴性反应,呈单个细胞卵园和球形,菌落为玫瑰红色,湿润光滑,菌体液体培养物为深红色,液体培养后的菌悬液含单个菌量为2.6-2.8亿个/mL,经鉴定为Rhodobacter sphaeroides,Rhodobacter palustri s,Rhodobacter Capsulatus,Rhodospirillum rubrum等菌株。Photosynthetic bacteria (photosynthetic bacteria referred to as PSB) were isolated in Xiaoyuehe, Beijing. The medium used for isolation was: organic matter 1.5-2g, (NH 4 ) 2 SO 4 1g, NaCl 2g, NaCO 3 5g, K 2 HPO 4 0.5g, MgSO 4 ·7H 2 O0.2g, distilled water 1000mL, pH 7.0, culture at 25-30℃ under light. The isolated PSB has a Gram-negative reaction and is single-cell egg garden and spherical. The colony is rose red, moist and smooth, and the liquid culture of the bacteria is dark red. The bacterial suspension after liquid culture contains 2.6- 280 million/mL, identified as Rhodobacter sphaeroides, Rhodobacter palustri s, Rhodobacter Capsulatus, Rhodospirillum rubrum and other strains.
光合微生物燃料电池由阴极、阳极两个电极室构成,通过质子交换膜(Nation-117,Dupont)连接,质子交换膜与两极室之间夹有真空垫以保持密封,每个电极室装入1000ml溶液。阳极板物理表面积90cm2,两块,串联使用。阳极室加入阳极缓冲液(表3)及Zarrouk氏培养基,阴极室加入阴极缓冲液(表4)。所有装置均置于光照培养箱中进行实验。生长温度在25-30℃,光照强度4.9×103lx,负载电阻确定为530Ω。The photosynthetic microbial fuel cell consists of two electrode chambers, the cathode and the anode, which are connected by a proton exchange membrane (Nation-117, Dupont). A vacuum pad is sandwiched between the proton exchange membrane and the bipolar chambers to keep it sealed. Each electrode chamber is filled with 1000ml solution. The physical surface area of the anode plate is 90cm 2 , two pieces are used in series. Anode buffer (Table 3) and Zarrouk's medium were added to the anode chamber, and cathode buffer (Table 4) was added to the cathode chamber. All devices were placed in a light incubator for experiments. The growth temperature is 25-30°C, the light intensity is 4.9×10 3 lx, and the load resistance is determined to be 530Ω.
电极预先放入培养皿中进行PSB富集,形成成熟生物膜后,将阳极插入极室时,电压迅速上升到0.25V左右,见图4。将取自北京市高碑店污水处理厂沉淀池中的污水30ml,COD=321.2mg/L,加入阳极。电压迅速升至0.31V左右,随着污水的降解电压不断下降,COD也不断下降。当电压降至0.25V时,再加入上述污水,电压又迅速上升至0.31V,重复上述过程。处理5天污水的COD可由321.2mg/L降低到122.6mg/L,去除率达到61.8%,且产生氢气1.6升。The electrode is placed in a petri dish in advance for PSB enrichment. After the mature biofilm is formed, when the anode is inserted into the electrode chamber, the voltage rises rapidly to about 0.25V, as shown in Figure 4. Add 30ml of sewage, COD=321.2mg/L, from the sedimentation tank of Beijing Gaobeidian Sewage Treatment Plant to the anode. The voltage rises rapidly to around 0.31V, and as the sewage degrades, the voltage continues to drop, so does the COD. When the voltage drops to 0.25V, the above-mentioned sewage is added again, and the voltage rises rapidly to 0.31V, and the above process is repeated. The COD of sewage treated for 5 days can be reduced from 321.2mg/L to 122.6mg/L, the removal rate reaches 61.8%, and 1.6 liters of hydrogen is produced.
实施例3:Example 3:
光合微生物为螺旋藻,采用Zarrouk氏培养基,250mL三角瓶内加入150mL培养液,接种对数生长期螺旋藻,起始浓度750nm吸收值为0.05-0.1,呈微淡绿色,调整培养液pH值至10左右,THZ-82型恒温摇床振荡器30℃、24h·d-1光照摇瓶培养。The photosynthetic microorganism is Spirulina, using Zarrouk's medium, adding 150mL of culture medium into a 250mL Erlenmeyer flask, and inoculating Spirulina in the logarithmic growth phase. To 10 or so, THZ-82 type constant temperature shaker shaker 30 ℃, 24h · d -1 light shake flask culture.
光合微生物燃料电池由阴极、阳极两个电极室构成,通过质子交换膜(Nation-117,Dupont)连接,质子交换膜与两极室之间夹有真空垫以保持密封,每个电极室装入1000ml溶液。阳极板物理表面积120cm2,阳极室加入阳极缓冲液(表3)及Zarrouk氏培养基,阴极室加入阴极缓冲液(表4)。所有装置均置于光照培养箱中进行实验。生长温度在25-30℃,光照强度4.7×103lx,负载电阻确定为520Ω。The photosynthetic microbial fuel cell consists of two electrode chambers, the cathode and the anode, which are connected by a proton exchange membrane (Nation-117, Dupont). A vacuum pad is sandwiched between the proton exchange membrane and the bipolar chambers to keep it sealed. Each electrode chamber is filled with 1000ml solution. The physical surface area of the anode plate is 120 cm 2 , the anode chamber is filled with anode buffer (Table 3) and Zarrouk's medium, and the cathode chamber is filled with cathode buffer (Table 4). All devices were placed in a light incubator for experiments. The growth temperature is 25-30°C, the light intensity is 4.7×10 3 lx, and the load resistance is determined to be 520Ω.
电极预先放入培养皿中进行螺旋藻富集,形成成熟生物膜后,将阳极插入极室时,电压迅速上升到0.18V左右,见图5。将取自某矿山的金属-有机复合废水,其成份见表5,取20ml加入阳极,电压快速升至0.26V左右,随着污水的降解电压不断下降,COD也不断下降。当电压降至0.18V时,再加入上述污水,电压又迅速上升至0.26V,重复上述过程。处理8天污水的COD可由820mg/L降低到125.8mg/L,去除率达到84.8%。8天后即可从阳极收获螺旋藻6.2克,且产生沼气1升。The electrodes are pre-placed in a Petri dish for enrichment of spirulina. After forming a mature biofilm, when the anode is inserted into the electrode chamber, the voltage rises rapidly to about 0.18V, as shown in Figure 5. The composition of metal-organic composite wastewater from a certain mine is shown in Table 5. Take 20ml and add it to the anode, and the voltage quickly rises to about 0.26V. As the degradation voltage of sewage continues to decrease, the COD also decreases. When the voltage drops to 0.18V, the above sewage is added again, and the voltage rises rapidly to 0.26V, and the above process is repeated. The COD of sewage treated for 8 days can be reduced from 820mg/L to 125.8mg/L, and the removal rate reaches 84.8%. After 8 days, 6.2 grams of Spirulina can be harvested from the anode, and 1 liter of biogas can be produced.
表5金属-有机物复合污染处理结果Table 5 Treatment results of metal-organic compound pollution
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