CN114122569B - Hydride/air battery for simultaneous treatment of waste acid and waste alkali and generation of electricity - Google Patents
Hydride/air battery for simultaneous treatment of waste acid and waste alkali and generation of electricity Download PDFInfo
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- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
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- C—CHEMISTRY; METALLURGY
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- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
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Abstract
Description
技术领域Technical Field
本发明是一种涉及化工、环境和能源领域的技术,具体是一种基于安全的同步处理废酸废碱并产电的氢化物/空气电池的装置及方法。The present invention relates to a technology related to the fields of chemical industry, environment and energy, and specifically to a device and method for a hydride/air battery for safely and simultaneously treating waste acid and waste alkali and generating electricity.
背景技术Background Art
工业生产中排放的废酸废碱对我们的水体环境影响极大,是制约我国可持续发展的一个突出问题。传统处理废酸废碱的技术包括直接混合废酸废碱中和、生物技术、水泥窑高温焚毁、气浮沉淀除杂、铁炭微电解、湿式氧化法处理技术。然而,这些传统技术方法资源利用率低,缺乏经济效益。例如,直接混合中和处理技术是将酸性废水与碱性废水互相混合中和或者用固体废碱渣直接中和酸性废水。但是,该技术的化学中和过程中所产生的废热能量并没有加以转化利用,导致总利用率和经济效益较低。Waste acids and alkalis discharged from industrial production have a great impact on our water environment and are a prominent problem restricting my country's sustainable development. Traditional technologies for treating waste acids and alkalis include direct mixing of waste acids and alkalis for neutralization, biotechnology, high-temperature incineration in cement kilns, flotation precipitation and impurity removal, iron-carbon micro-electrolysis, and wet oxidation treatment technology. However, these traditional technical methods have low resource utilization and lack economic benefits. For example, direct mixing and neutralization treatment technology is to mix acidic wastewater and alkaline wastewater for neutralization or to directly neutralize acidic wastewater with solid waste alkali residue. However, the waste heat energy generated in the chemical neutralization process of this technology has not been converted and utilized, resulting in low overall utilization and economic benefits.
发明内容Summary of the invention
本发明针对目前安全性高、资源化利用率高的废酸废碱同步处理技术缺乏的问题,提出一种同步处理废酸废碱并产生电能的金属氢化物/空气电化学电池装置。该技术发明利用安全性高的氢化物在碱性条件下消耗OH-离子的氧化反应作为负极反应和安全性高的空气扩散电极在酸性条件下消耗H+离子的还原反应作为正极反应,酸碱电解液由离子交换膜隔开。在放电或进行电化学中和的过程中,即处理废酸废碱的同时,可从废酸废碱处理过程中获取电能,实现高效安全及资源化利用的电化学中和处理。本发明废酸废碱处理过程中不排放废气废液,并可连续性处理废酸和废碱。本发明为工业生产中产生的废酸废碱带来的环境污染问题上提供一种“无害化、减量化和资源化”处理技术路径,具有现实意义和良好的应用前景。The present invention aims at the problem that there is a lack of technology for simultaneous treatment of waste acid and waste alkali with high safety and high resource utilization rate at present, and proposes a metal hydride/air electrochemical battery device for simultaneous treatment of waste acid and waste alkali and generation of electric energy. The technical invention utilizes the oxidation reaction of the highly safe hydride consuming OH- ions under alkaline conditions as the negative electrode reaction and the reduction reaction of the highly safe air diffusion electrode consuming H + ions under acidic conditions as the positive electrode reaction, and the acid-base electrolyte is separated by an ion exchange membrane. During the discharge or electrochemical neutralization process, that is, while treating the waste acid and waste alkali, electric energy can be obtained from the waste acid and waste alkali treatment process, thereby realizing efficient, safe and resource-utilized electrochemical neutralization treatment. In the process of treating the waste acid and waste alkali of the present invention, no waste gas and waste liquid are discharged, and the waste acid and waste alkali can be continuously treated. The present invention provides a "harmless, reduced and resource-utilized" treatment technology path for the environmental pollution caused by the waste acid and waste alkali generated in industrial production, which has practical significance and good application prospects.
本发明是通过以下技术方案实现的:The present invention is achieved through the following technical solutions:
本发明涉及一种同步处理废酸废碱并产生电能的金属氢化物/空气电化学电池装置,包括:作为正极的空气扩散电极、作为负极的预储氢的氢化物电极以及离子交换膜,其中:正、负极分别置于废酸溶液和废碱溶液中且正、负极与外电路相连,离子交换膜设置于酸碱两种电解液间作为隔膜材料;当电池放电或进行废酸废碱处理时,负极发生的反应为析出氢并与废碱中的OH-离子发生氧化反应,生成水并产出电子;同时电子从外电路导出并流向正极,使得空气中的氧气与废酸中的H+离子发生还原反应生成水。The invention relates to a metal hydride/air electrochemical battery device for simultaneously treating waste acid and waste alkali and generating electric energy, comprising: an air diffusion electrode as a positive electrode, a hydride electrode for pre-storing hydrogen as a negative electrode, and an ion exchange membrane, wherein: the positive electrode and the negative electrode are respectively placed in a waste acid solution and a waste alkali solution and are connected to an external circuit, and the ion exchange membrane is arranged between the acid and alkali electrolytes as a diaphragm material; when the battery is discharged or the waste acid and waste alkali are treated, the reaction occurring at the negative electrode is hydrogen precipitation and oxidation reaction with OH- ions in the waste alkali to generate water and produce electrons; at the same time, the electrons are led out of the external circuit and flow to the positive electrode, so that oxygen in the air and H + ions in the waste acid undergo reduction reaction to generate water.
本装置的上述整个放电过程中,H+离子和OH-离子得到了有效的电化学中和处理并通过相应的电化学反应释放电能。During the above-mentioned whole discharge process of the device, H + ions and OH- ions are effectively electrochemically neutralized and release electric energy through corresponding electrochemical reactions.
所述的废酸溶液和废碱溶液可取自工业上所产生废酸废碱,并直接用作本发明电化学电池装置的电解液,在得到电化学中和处理的同时获取电能。The waste acid solution and waste alkali solution can be taken from waste acid and waste alkali produced in industry, and directly used as the electrolyte of the electrochemical cell device of the present invention, and electric energy is obtained while being electrochemically neutralized.
所述的空气扩散电极,通过将铂碳催化剂、导电碳黑与粘结剂溶液混合研磨后涂于疏水碳布表面烘干得到。The air diffusion electrode is obtained by mixing and grinding a platinum-carbon catalyst, conductive carbon black and a binder solution, applying the mixture on the surface of a hydrophobic carbon cloth and drying the mixture.
所述的预储氢的氢化物电极,通过以下步骤得到:The hydride electrode for pre-storing hydrogen is obtained by the following steps:
①将镍氢电池中成分为LaNi5的金属氢化物(MH)、导电碳黑和粘结剂溶液混合研磨后烘干得到活性物质;① The active material is obtained by mixing and grinding the metal hydride (MH) of LaNi 5 in the nickel-hydrogen battery, conductive carbon black and a binder solution, and then drying;
②将活性物质涂抹于泡沫镍上后将泡沫镍对折并将镀镍钢带夹于中间形成夹心结构且镀镍钢带部分伸出泡沫镍外。② After applying the active substance on the nickel foam, fold the nickel foam in half and sandwich the nickel-plated steel strip in the middle to form a sandwich structure with the nickel-plated steel strip partially extending out of the nickel foam.
③夹心结构烘干并压实后进行活化处理。③ The sandwich structure is dried and compacted before being activated.
所述的金属氢化物的成分为LaNi5镧镍储氢合金。The metal hydride is composed of LaNi 5 lanthanum nickel hydrogen storage alloy.
所述的活化处理是指:以20mA电流进行充放电(充电时间为2小时,放电截止电压为0.2伏),共循环四次,并最终进行一次充电(截止电压为1.5伏)形成预储氢的氢化物电极。The activation treatment refers to: charging and discharging with a current of 20 mA (charging time is 2 hours, discharge cut-off voltage is 0.2 volts), a total of four cycles, and finally charging once (cut-off voltage is 1.5 volts) to form a hydride electrode for pre-storing hydrogen.
所述的废酸溶液,优选在处理前pH值小于1,经处理后实现废酸中氢离子的浓度降低,具体为每产出87.5毫安时电量,至少对应0.15-0.21M的氢离子浓度降幅。处理后的废酸溶液pH值上升,意味着酸性明显减弱。The waste acid solution preferably has a pH value of less than 1 before treatment, and after treatment, the concentration of hydrogen ions in the waste acid is reduced, specifically, for every 87.5 mAh of electricity produced, the hydrogen ion concentration decreases by at least 0.15-0.21 M. The increase in the pH value of the waste acid solution after treatment means that the acidity is significantly weakened.
所述的废碱溶液,优选在处理前pH值大于13,经处理后实现实现废碱中氢氧根离子的浓度降低,具体为每产出87.5毫安时电量,至少对应0.15-0.21M的氢氧根离子浓度降幅。废碱溶液在处理后的pH值下降,意味着碱性明显减弱。The waste alkali solution preferably has a pH value greater than 13 before treatment, and after treatment, the concentration of hydroxide ions in the waste alkali is reduced, specifically, for every 87.5 mAh of electricity produced, the concentration of hydroxide ions decreases by at least 0.15-0.21 M. The decrease in the pH value of the waste alkali solution after treatment means that the alkalinity is significantly weakened.
所述的电池放电,总反应为1摩尔的氧气、4摩尔的氢离子、4摩尔预储氢的氢化物和4摩尔的氢氧根离子生成4摩尔的释放氢后的氢化物和6摩尔的水,反应产物中无任何废气废液产生。The battery discharges, and the total reaction is 1 mole of oxygen, 4 moles of hydrogen ions, 4 moles of hydride pre-stored with hydrogen and 4 moles of hydroxide ions to generate 4 moles of hydride after hydrogen is released and 6 moles of water, and no waste gas or waste liquid is generated in the reaction products.
所述的同步处理废酸废碱并产电的氢化物/空气电池放电反应机理,具体包括:The discharge reaction mechanism of the hydride/air battery for simultaneously treating waste acid and waste alkali and generating electricity specifically includes:
正极反应: Positive electrode reaction:
负极反应: Negative electrode reaction:
总反应: Overall reaction:
技术效果Technical Effects
本发明利用安全性高的氢化物储氢材料在碱性条件下消耗OH-离子的氧化反应作为负极反应和安全性高的空气扩散电极在酸性条件下消耗H+离子的还原反应作为正极反应,并用离子交换膜隔开酸碱电解液防止直接混合化学中和反应,所形成电化学电池装置的总电化学反应能够电化学中和H+离子和OH-离子并产出水和电量。其与现有技术相比,负极采用安全性高的常温金属氢化物储氢材料,极大地提高了实际工业生产操作的安全性;液态产物仅为水,不排放废气废液,绿色环保;基于两腔室及酸碱电极配对的电池结构设计改进,可针对多种不同pH值的废液处理问题;通过新型电化学反应的方式实现同步电化学中和处理废酸废碱两种液并产电,提高了资源化利用率。The present invention utilizes the oxidation reaction of the highly safe hydride hydrogen storage material under alkaline conditions to consume OH- ions as the negative electrode reaction and the reduction reaction of the highly safe air diffusion electrode under acidic conditions to consume H + ions as the positive electrode reaction, and uses an ion exchange membrane to separate the acid-base electrolyte to prevent direct mixing of chemical neutralization reactions. The total electrochemical reaction of the electrochemical battery device formed can electrochemically neutralize H + ions and OH- ions and produce water and electricity. Compared with the prior art, the negative electrode adopts a highly safe room-temperature metal hydride hydrogen storage material, which greatly improves the safety of actual industrial production operations; the liquid product is only water, and no waste gas or waste liquid is discharged, which is green and environmentally friendly; the battery structure design based on the two chambers and acid-base electrode pairing can be used to treat waste liquids with different pH values; the synchronous electrochemical neutralization treatment of waste acid and waste alkali liquids and the generation of electricity are achieved through a new electrochemical reaction method, which improves the resource utilization rate.
基于正、负极的标准电极电位,当氢离子和氢氧根离子浓度各为1M时,在标准条件下该发明电池理论上可产出2.03伏的电压。本发明所形成的电化学电池装置实际开路电压测定值高于1.6伏。另外,废酸中的氢离子和废碱中的氢氧根离子均在放电过程中得到有效的中和处理并产出电量。所以,该发明电池装置具备高效同步处理废酸废碱并利用处理过程中产生的电量的优势特点。典型技术效果为:电化学电池装置同步处理氢离子浓度和氢氧根离子各0.15-0.21M,可产生电量87.5毫安时,两废液的酸碱性分别明显减弱。Based on the standard electrode potential of the positive and negative electrodes, when the concentrations of hydrogen ions and hydroxide ions are 1M each, the battery of the invention can theoretically produce a voltage of 2.03 volts under standard conditions. The actual open circuit voltage measurement value of the electrochemical battery device formed by the present invention is higher than 1.6 volts. In addition, the hydrogen ions in the waste acid and the hydroxide ions in the waste alkali are effectively neutralized and produce electricity during the discharge process. Therefore, the battery device of the invention has the advantages of efficiently and simultaneously treating waste acid and waste alkali and utilizing the electricity generated during the treatment process. The typical technical effect is: the electrochemical battery device simultaneously treats hydrogen ion concentrations and hydroxide ions of 0.15-0.21M each, which can generate 87.5 mAh of electricity, and the acidity and alkalinity of the two waste liquids are significantly weakened.
附图说明BRIEF DESCRIPTION OF THE DRAWINGS
图1为氢化物/空气电池的放电反应机理图;FIG1 is a diagram showing the discharge reaction mechanism of a hydride/air battery;
图2为实施例1和实施例2中电池电流测试中电压随时间变化对比图;FIG2 is a comparison diagram of voltage changes over time in battery current tests in Example 1 and Example 2;
图3为实施例3电池5-100mA电流测试极化曲线图;FIG3 is a polarization curve diagram of a battery in Example 3 at 5-100 mA current test;
图4为实施例4电池5-70mA电流测试极化曲线图;FIG4 is a polarization curve diagram of a battery in Example 4 under a current test of 5-70 mA;
图5为同步处理废酸废碱并产电的氢化物/空气电池结构图;FIG5 is a structural diagram of a hydride/air battery that simultaneously treats waste acid and waste alkali and generates electricity;
图中:空气扩散电极1、气体扩散层101、催化剂层102、离子交换膜2、金属氢化物3、外部电路4;In the figure: air diffusion electrode 1, gas diffusion layer 101, catalyst layer 102, ion exchange membrane 2, metal hydride 3, external circuit 4;
图6为实施例的实际工作装置图;Fig. 6 is a diagram of the actual working device of the embodiment;
图中:空气扩散电极1、气体扩散层101、催化剂层102、离子交换膜2、系有镀镍钢带并浸泡于碱性溶液里的金属氢化物电极3、装有与空气扩散电极的催化剂层相接触的酸性溶液的铁氟龙腔体4、允许空气与空气扩散电极的气体扩散层相接触的铁氟龙腔体5、与空气扩散电极催化剂层接触并导电的不锈钢带集流体6。In the figure: an air diffusion electrode 1, a gas diffusion layer 101, a catalyst layer 102, an ion exchange membrane 2, a metal hydride electrode 3 with a nickel-plated steel strip and immersed in an alkaline solution, a Teflon cavity 4 filled with an acidic solution in contact with the catalyst layer of the air diffusion electrode, a Teflon cavity 5 allowing air to contact the gas diffusion layer of the air diffusion electrode, and a stainless steel strip current collector 6 in contact with the catalyst layer of the air diffusion electrode and conducting electricity.
具体实施方式DETAILED DESCRIPTION
实施例1Example 1
本实施例包括以下工艺和测试步骤:This embodiment includes the following process and testing steps:
1)电解液的制备:配置0.5M的硫酸35mL作为模拟废酸正极电解液。配置1M的KOH溶液35mL作为模拟废碱负极电解液。1) Preparation of electrolyte: Prepare 35 mL of 0.5 M sulfuric acid as the simulated spent acid positive electrolyte and 35 mL of 1 M KOH solution as the simulated spent alkali negative electrolyte.
2)正极电极的制备:将30mg铂碳催化剂与0.4mL50wt%聚四氟乙烯(PTFE)粘接剂溶液混合研磨后涂于疏水碳布表面,置于80℃烘箱中2h。2) Preparation of positive electrode: 30 mg of platinum-carbon catalyst was mixed with 0.4 mL of 50 wt% polytetrafluoroethylene (PTFE) adhesive solution, ground and coated on the surface of hydrophobic carbon cloth, and placed in an oven at 80° C. for 2 h.
3)负极电极的制备:从放电完全的可充电电池中取出金属氢化物(MH),将1gMH、50mg碳黑(卡博特)、1mL50wt%PTFE溶液混合研磨后,放入烘箱中烘干至水泥状,得到活性物质,将活性物质涂抹于3*6cm,厚度为0.5mm泡沫镍的上半面上,剪取6cm长、厚宽为0.15*8mm的镀镍钢带,将泡沫镍对折,将活性物质与镀镍钢带夹于中间,镀镍钢带部分伸出泡沫镍外作为导线集流体,由此制得负极电极。将电极置于80℃烘箱中2h,取出后用压力机以45KPa的压力压20min。3) Preparation of negative electrode: Take out metal hydride (MH) from a fully discharged rechargeable battery, mix and grind 1g MH, 50mg carbon black (Cabot), and 1mL 50wt% PTFE solution, put it in an oven and dry it to cement, to obtain an active material, apply the active material on the upper half of a 3*6cm, 0.5mm thick nickel foam, cut a 6cm long, 0.15*8mm thick nickel-plated steel strip, fold the nickel foam in half, sandwich the active material and the nickel-plated steel strip in the middle, and partially extend the nickel-plated steel strip outside the nickel foam as a conductor current collector, thereby preparing a negative electrode. The electrode was placed in an oven at 80°C for 2h, and after being taken out, it was pressed with a press at a pressure of 45KPa for 20min.
4)负极电极的活化:从放电完全的可充电电池中取出正极(其成分为氢氧化镍),以1M的KOH溶液作为电解液,与步骤3)中制得的负极电极共同组成二次电池,以20mA电流进行充放电,循环四次,最后以20mA电流进行充电至1.5V,得到活化并充电完全的负极电极。4) Activation of the negative electrode: Take out the positive electrode (whose component is nickel hydroxide) from the fully discharged rechargeable battery, use 1M KOH solution as electrolyte, and form a secondary battery together with the negative electrode prepared in step 3), charge and discharge at a current of 20mA, cycle four times, and finally charge to 1.5V at a current of 20mA to obtain an activated and fully charged negative electrode.
5)隔膜材料处理和电池组装:将从5wt%NaCl溶液中取出浸泡超12小时的阳离子交换膜,用去离子水洗净。正极腔室内装有正极电解液;负极腔室内装有负极电解液,处于静态;正极腔室的两侧分别为负极腔室和空气腔室。正、负极电解液通过离子交换膜进行隔离,避免直接接触化学中和。将步骤1)、2)、4)、5)所得到的关键材料装配成电池待测试,正、负极集流体分别为不锈钢带和镀镍钢带。5) Diaphragm material processing and battery assembly: Take out the cation exchange membrane soaked in 5wt% NaCl solution for more than 12 hours and wash it with deionized water. The positive electrode chamber is filled with positive electrode electrolyte; the negative electrode chamber is filled with negative electrode electrolyte and is in a static state; the two sides of the positive electrode chamber are the negative electrode chamber and the air chamber respectively. The positive and negative electrode electrolytes are separated by an ion exchange membrane to avoid direct contact and chemical neutralization. The key materials obtained in steps 1), 2), 4) and 5) are assembled into batteries for testing. The positive and negative electrode current collectors are stainless steel strips and nickel-plated steel strips respectively.
电流测试:用武汉蓝电电池测试系统从5mA至35mA,每隔5mA连续恒流放电5min,并每间隔10s测量开路电压。利用数显pH计直接测量完成测试后的电解液的pH值。Current test: Use Wuhan Blue Electric Battery Test System to discharge the battery continuously at a constant current of 5 mA from 5 mA to 35 mA for 5 minutes, and measure the open circuit voltage every 10 seconds. Use a digital pH meter to directly measure the pH value of the electrolyte after the test.
本实施例中,pH值变化如下表1所示。pH有显著变化,具体数值为:酸性溶液的pH值从0.63上升到1.14,而碱性溶液的pH值从13.65下降到12.89,pH变化值分别为0.51和0.76。因此,氢离子/氢氧根离子均有一定消耗,表明该电池能够放电并能中和相应部分的废酸废碱溶液。本实施例中的电化学电池装置产电量约12毫安时。In this embodiment, the pH value changes as shown in Table 1 below. The pH changes significantly, with specific values as follows: the pH value of the acidic solution rises from 0.63 to 1.14, while the pH value of the alkaline solution drops from 13.65 to 12.89, with pH change values of 0.51 and 0.76, respectively. Therefore, hydrogen ions/hydroxyl ions are consumed to a certain extent, indicating that the battery can discharge and neutralize the corresponding portion of the waste acid and waste alkali solution. The electrochemical battery device in this embodiment produces about 12 milliampere hours of electricity.
实施例2Example 2
本实施例中包括以下工艺和测试步骤:This embodiment includes the following process and testing steps:
1)电解液的制备:配置1M的硫酸35mL作为模拟废酸正极电解液。配置1M的KOH溶液35mL作为模拟废碱负极电解液。区别于实施例1,本实施例使用酸性更高的废酸溶液来进一步证明该电池的实用性。1) Preparation of electrolyte: 35 mL of 1M sulfuric acid was prepared as a simulated waste acid positive electrode electrolyte. 35 mL of 1M KOH solution was prepared as a simulated waste alkali negative electrode electrolyte. Different from Example 1, this example uses a more acidic waste acid solution to further demonstrate the practicality of the battery.
2)正极电极的制备:将30mg铂碳催化剂与0.4mL50wt%PTFE粘接剂溶液混合研磨后涂于疏水碳布表面,置于80℃烘箱中2h。2) Preparation of positive electrode: 30 mg of platinum-carbon catalyst was mixed with 0.4 mL of 50 wt% PTFE adhesive solution, ground and coated on the surface of hydrophobic carbon cloth, and placed in an oven at 80° C. for 2 h.
3)负极电极的制备:从放电完全的可充电电池中取出金属氢化物(MH),将1gMH、50mg碳黑(卡博特)、1mL50wt%PTFE溶液混合研磨后,放入烘箱中烘干至水泥状,得到活性物质,将活性物质涂抹于3*6cm,厚度为0.5mm泡沫镍的上半面上,剪取6cm长、厚宽为0.15*8mm的镀镍钢带,将泡沫镍对折,将活性物质与镀镍钢带夹于中间,镀镍钢带部分伸出泡沫镍外,由此制得负极电极作为导线集流体。将电极置于80℃烘箱中2h,取出后用压力机以45MPa的压力压20min。区别于实施例1,本实施例使用更高压力对电极进行制备,以此进一步提高电极性能。3) Preparation of negative electrode: Take out metal hydride (MH) from a fully discharged rechargeable battery, mix and grind 1g MH, 50mg carbon black (Cabot), and 1mL 50wt% PTFE solution, put it in an oven and dry it to cement to obtain an active material, apply the active material on the upper half of a 3*6cm, 0.5mm thick nickel foam, cut a 6cm long, 0.15*8mm thick nickel-plated steel strip, fold the nickel foam in half, sandwich the active material and the nickel-plated steel strip in the middle, and partially extend the nickel-plated steel strip out of the nickel foam, thereby preparing a negative electrode as a conductor current collector. The electrode was placed in an oven at 80°C for 2h, and after being taken out, it was pressed with a press at a pressure of 45MPa for 20min. Different from Example 1, this embodiment uses a higher pressure to prepare the electrode to further improve the electrode performance.
4)负极电极的活化:从放电完全的可充电电池中取出正极(成分为氢氧化镍),以1M的KOH溶液作为电解液,与步骤3)中制得的负极电极共同组成二次电池,以20mA电流进行充放电,循环四次,最后以20mA电流进行充电至1.5V,得到活化并充电完全的负极电极。4) Activation of the negative electrode: Take out the positive electrode (composed of nickel hydroxide) from the fully discharged rechargeable battery, use 1M KOH solution as the electrolyte, and form a secondary battery together with the negative electrode prepared in step 3), charge and discharge at a current of 20mA, cycle four times, and finally charge to 1.5V at a current of 20mA to obtain an activated and fully charged negative electrode.
5)隔膜材料处理和电池组装:将从5wt%NaCl溶液中取出浸泡超12小时的阳离子交换膜,用去离子水洗净。正极腔室内装有正极电解液;负极腔室内装有负极电解液,处于静态;正极腔室的两侧分别为负极腔室和空气腔室。正、负极电解液通过离子交换膜进行隔离避免直接接触。将步骤1)、2)、4)、5)所得到的关键材料装配成电池待测试,正、负极集流体分别为不锈钢带和镀镍钢带。5) Diaphragm material processing and battery assembly: Take out the cation exchange membrane soaked in 5wt% NaCl solution for more than 12 hours and wash it with deionized water. The positive electrode chamber is filled with positive electrode electrolyte; the negative electrode chamber is filled with negative electrode electrolyte and is in a static state; the two sides of the positive electrode chamber are the negative electrode chamber and the air chamber respectively. The positive and negative electrode electrolytes are isolated by an ion exchange membrane to avoid direct contact. The key materials obtained in steps 1), 2), 4) and 5) are assembled into batteries for testing, and the positive and negative electrode current collectors are stainless steel strips and nickel-plated steel strips respectively.
电流测试:用武汉蓝电电池测试系统从5mA至35mA,每隔5mA连续恒流放电5min,并每间隔10s测量开路电压。利用数显pH计直接测量完成测试后的电解液的pH值。Current test: Use Wuhan Blue Electric Battery Test System to discharge the battery continuously at a constant current of 5 mA from 5 mA to 35 mA for 5 minutes, and measure the open circuit voltage every 10 seconds. Use a digital pH meter to directly measure the pH value of the electrolyte after the test.
本实施例中,pH变化如下表2所示。pH有显著变化,具体数值为:酸性溶液的pH值从0.34上升到0.73,而碱性溶液的pH值从13.46下降到12.89,pH变化值分别为0.39和0.57。因此,氢离子/氢氧根离子均有一定消耗,表明该电池能够放电并能中和相应部分的酸碱溶液。本实施例中的电化学电池装置产电量约12毫安时。In this embodiment, the pH changes are shown in Table 2 below. The pH changes significantly, with specific values as follows: the pH value of the acidic solution increases from 0.34 to 0.73, while the pH value of the alkaline solution decreases from 13.46 to 12.89, with pH change values of 0.39 and 0.57, respectively. Therefore, both hydrogen ions and hydroxide ions are consumed to a certain extent, indicating that the battery can discharge and neutralize the corresponding portion of the acid and alkaline solution. The electrochemical battery device in this embodiment produces about 12 mAh of electricity.
实施例1和2的电压随时间变化曲线如图2所示,图中Voltage1实验数据为实施例1所得,而Voltage2实验数据为实施例2所得。实施例2中压制负极所用压力增大后使得材料的结构更紧凑,不易脱落,电池的性能更加稳定,具体表现为其放电平台在所测试的电流范围内均高于1.4伏。The voltage variation curves of Examples 1 and 2 over time are shown in FIG2 , where the experimental data of Voltage 1 are obtained in Example 1, and the experimental data of Voltage 2 are obtained in Example 2. In Example 2, the increased pressure used to press the negative electrode makes the material structure more compact and less likely to fall off, and the battery performance is more stable, which is specifically manifested in that the discharge platform is higher than 1.4 volts within the tested current range.
实施例3Example 3
本实施例包括以下工艺和测试步骤:This embodiment includes the following process and testing steps:
1)电解液的制备:配置1M的硫酸17mL作为模拟废酸正极电解液。配置1M的KOH溶液17mL作为模拟废碱负极电解液。本实施例使用更少的电解液,以此来探究电池装置的实用性。1) Preparation of electrolyte: 17 mL of 1M sulfuric acid was prepared as a simulated waste acid positive electrolyte. 17 mL of 1M KOH solution was prepared as a simulated waste alkali negative electrolyte. This example uses less electrolyte to explore the practicality of the battery device.
2)正极电极的制备:将30mg铂碳催化剂与0.4mL50wt%PTFE粘接剂溶液混合研磨后涂于碳布表面,置于80℃烘箱中2h。2) Preparation of positive electrode: 30 mg of platinum-carbon catalyst was mixed with 0.4 mL of 50 wt% PTFE adhesive solution, ground and coated on the surface of carbon cloth, and placed in an oven at 80° C. for 2 h.
3)负极电极的制备:从放电完全的可充电电池中取出金属氢化物(MH),将1gMH、50mg碳黑(卡博特)、1mL50wt%PTFE溶液混合研磨后,放入烘箱中烘干至水泥状,得到活性物质,将活性物质涂抹于3*6cm,厚度为2mm泡沫镍的上半面上,剪取6cm长、厚宽为0.15*8mm的镀镍钢带,将泡沫镍对折,将活性物质与镀镍钢带夹于中间,镀镍钢带部分伸出泡沫镍外作为导线集流体,由此制得负极电极。将电极置于80℃烘箱中2h,取出后用压力机以45MPa的压力压20min。区别于实施例1和2,本实施例使用更厚的泡沫镍对电极进行制备,以此进一步提高电极性能。3) Preparation of negative electrode: Take out metal hydride (MH) from a fully discharged rechargeable battery, mix and grind 1g MH, 50mg carbon black (Cabot), and 1mL 50wt% PTFE solution, put it in an oven and dry it to cement to obtain an active material, apply the active material on the upper half of a 3*6cm, 2mm thick nickel foam, cut a 6cm long, 0.15*8mm thick nickel-plated steel strip, fold the nickel foam in half, sandwich the active material and the nickel-plated steel strip in the middle, and partially extend the nickel-plated steel strip outside the nickel foam as a conductor current collector, thereby preparing a negative electrode. Place the electrode in an oven at 80°C for 2h, take it out and press it with a press at a pressure of 45MPa for 20min. Different from Examples 1 and 2, this embodiment uses thicker nickel foam to prepare the electrode, so as to further improve the electrode performance.
4)负极电极的活化:从放电完全的可充电电池中取出正极(其成分为氢氧化镍),以1M的KOH溶液作为电解液,与步骤3)中制得的负极电极共同组成二次电池,以20mA电流进行充放电,循环四次,最后以20mA电流进行充电至1.6V,得到活化并充电完全的电极负极。4) Activation of the negative electrode: Take out the positive electrode (whose component is nickel hydroxide) from the fully discharged rechargeable battery, use 1M KOH solution as electrolyte, and form a secondary battery together with the negative electrode prepared in step 3), charge and discharge at a current of 20mA, cycle four times, and finally charge to 1.6V at a current of 20mA to obtain an activated and fully charged electrode negative electrode.
5)隔膜材料处理和电池组装:将从5wt%NaCl溶液中取出浸泡超12小时的阴离子交换膜,用去离子水洗净。正极腔室内装有正极电解液;负极腔室内装有负极电解液,处于静态;正极腔室的两侧分别为负极腔室和空气腔室。正、负极电解液通过离子交换膜进行隔离避免直接接触。将步骤1)、2)、4)、5)所得到的关键材料装配成电池待测试,正、负极集流体分别为不锈钢带和镀镍钢带。区别于实施例1和2,本实施例使用阴离子交换膜作为隔膜材料,减缓H+离子的扩散,以此进一步提高电池性能。5) Diaphragm material processing and battery assembly: Take out the anion exchange membrane soaked in 5wt% NaCl solution for more than 12 hours and wash it with deionized water. The positive electrode chamber is filled with positive electrode electrolyte; the negative electrode chamber is filled with negative electrode electrolyte and is in a static state; the two sides of the positive electrode chamber are the negative electrode chamber and the air chamber respectively. The positive and negative electrode electrolytes are isolated by the ion exchange membrane to avoid direct contact. The key materials obtained in steps 1), 2), 4) and 5) are assembled into a battery for testing, and the positive and negative electrode current collectors are stainless steel strips and nickel-plated steel strips, respectively. Different from Examples 1 and 2, this embodiment uses anion exchange membrane as a diaphragm material to slow down the diffusion of H + ions, thereby further improving battery performance.
电流测试:用武汉蓝电电池测试系统从5mA至100mA,每隔5mA连续恒流放电5min,并每间隔10s测量开路电压。利用数显pH计和电导率仪分别测量完成测试后的电解液的pH值和导电率。Current test: Use Wuhan Blue Battery Test System to discharge the battery from 5mA to 100mA at a constant current of 5mA for 5 minutes, and measure the open circuit voltage every 10s. Use a digital pH meter and conductivity meter to measure the pH value and conductivity of the electrolyte after the test.
本实施例中,所形成的氢化物/空气电池稳定放电。其中,放电前酸性溶液的pH=0.13,电导率S=83.75mS/cm,碱性溶液的pH=13.56,电导率S=42.26mS/cm。放电后酸性溶液的pH=0.24,电导率S=62.26mS/cm,碱性溶液的pH=13.30,电导率S=22.61mS/cm。以上数据均表示酸性溶液和碱性溶液得到相应的电化学中和处理,酸碱性均显著减弱,并产出电量87.5毫安时。In this embodiment, the formed hydride/air battery discharges stably. Among them, the pH of the acidic solution before discharge is 0.13, the conductivity S is 83.75mS/cm, the pH of the alkaline solution is 13.56, and the conductivity S is 42.26mS/cm. After discharge, the pH of the acidic solution is 0.24, the conductivity S is 62.26mS/cm, and the pH of the alkaline solution is 13.30, and the conductivity S is 22.61mS/cm. The above data all indicate that the acidic solution and the alkaline solution are subjected to corresponding electrochemical neutralization treatment, the acidity and alkalinity are significantly weakened, and the output power is 87.5 mAh.
根据图3极化曲线可以得出,在输出电流稳定在90mA时,电池的输出功率最大,达到93mW。由法拉第定律计算得知,该电池的效率高达94%。这意味着94%的已电化学中和处理的废酸废碱均在该过程中产出了相应电量。According to the polarization curve in Figure 3, when the output current is stabilized at 90mA, the output power of the battery is the maximum, reaching 93mW. According to Faraday's law, the efficiency of the battery is as high as 94%. This means that 94% of the waste acid and alkali that have been electrochemically neutralized have produced corresponding electricity in the process.
实施例4Example 4
本实施例包括以下工艺和测试步骤:This embodiment includes the following process and testing steps:
1)电解液的制备:配置废酸模拟液17mL作为正极电解液,其成分为17wt%H2SO4、5wt%FeSO4、1.5wt%Al2(SO4)3、1wt%Ti(SO4)2;配置废碱模拟液80mL作为负极电解液,其成分为3wt%Na2CO3、0.5wt%NaHCO3、0.1wt%NaOH、0.5wt%NaClO。1) Preparation of electrolyte: 17 mL of waste acid simulation solution was prepared as the positive electrode electrolyte, and its composition was 17 wt% H 2 SO 4 , 5 wt% FeSO 4 , 1.5 wt% Al 2 (SO 4 ) 3 , 1 wt% Ti(SO 4 ) 2 ; 80 mL of waste alkali simulation solution was prepared as the negative electrode electrolyte, and its composition was 3 wt% Na 2 CO 3 , 0.5 wt% NaHCO 3 , 0.1 wt% NaOH, 0.5 wt% NaClO.
区别于实施例1,2和3,本实施例通过单侧废碱的流通循环电化学中和测试来验证本发明的可连续性处理能力和量化处理的可行性。Different from Examples 1, 2 and 3, this example verifies the continuous processing capability and feasibility of quantitative processing of the present invention through a circulation electrochemical neutralization test of single-side spent alkali.
2)正极电极的制备:将20mg铂碳催化剂、0.15g导电碳黑(卡博特)与0.4mL50wt%PTFE粘接剂溶液混合研磨后涂于碳布表面,置于80℃烘箱中2h。2) Preparation of positive electrode: 20 mg of platinum-carbon catalyst, 0.15 g of conductive carbon black (Cabot) and 0.4 mL of 50 wt% PTFE adhesive solution were mixed and ground, then applied to the surface of the carbon cloth and placed in an oven at 80°C for 2 h.
3)负极电极的制备:从放电完全的可充电电池中取出金属氢化物(MH),将1gMH、50mg导电碳黑(卡博特)、1mL50wt%PTFE溶液混合研磨后,放入烘箱中烘干至水泥状,得到活性物质,将活性物质涂抹于3*6cm,厚度为2mm泡沫镍的上半面上,剪取6cm长、厚宽为0.15*8mm的镀镍钢带,将泡沫镍对折,将活性物质与镀镍钢带夹于中间,镀镍钢带部分伸出泡沫镍外作为导线集流体,由此制得负极电极。将电极置于80℃烘箱中2h,取出后用压力机以45MPa的压力压20min。3) Preparation of negative electrode: Take out metal hydride (MH) from a fully discharged rechargeable battery, mix and grind 1g MH, 50mg conductive carbon black (Cabot), and 1mL 50wt% PTFE solution, put it in an oven and dry it to cement, to obtain an active material, apply the active material on the upper half of a 3*6cm, 2mm thick nickel foam, cut a 6cm long, 0.15*8mm thick nickel-plated steel strip, fold the nickel foam in half, sandwich the active material and the nickel-plated steel strip in the middle, and partially extend the nickel-plated steel strip outside the nickel foam as a conductor current collector, thereby preparing a negative electrode. The electrode was placed in an oven at 80°C for 2h, and after being taken out, it was pressed with a press at a pressure of 45MPa for 20min.
4)负极电极的活化:从放电完全的可充电电池中取出正极(其成分为氢氧化镍),以1M的KOH溶液作为电解液,与步骤3)中制得的负极电极共同组成二次电池,以20mA电流进行充放电,循环四次,最后以20mA电流进行充电至1.5V,得到活化并充电完全的负极电极。4) Activation of the negative electrode: Take out the positive electrode (whose component is nickel hydroxide) from the fully discharged rechargeable battery, use 1M KOH solution as electrolyte, and form a secondary battery together with the negative electrode prepared in step 3), charge and discharge at a current of 20mA, cycle four times, and finally charge to 1.5V at a current of 20mA to obtain an activated and fully charged negative electrode.
5)隔膜材料处理和电池组装:将从5wt%NaCl溶液中取出浸泡超12小时的阴离子交换膜,用去离子水洗净。正极腔室内装有正极电解液;负极腔室内装有负极电解液,由蠕动泵通过与电池的负极腔室入口和出口相连的硅胶管管路,并与外置的盛有负极电解液的烧杯接通,使负极电解液处于流动循环态;正极腔室的两侧分别为负极腔室和空气腔室。正、负极电解液通过离子交换膜进行隔离避免直接接触。将步骤1)、2)、4)、5)所得到的关键材料装配成电池待测试,正、负极集流体分别为不锈钢带和镀镍钢带。5) Diaphragm material processing and battery assembly: Take out the anion exchange membrane soaked for more than 12 hours from the 5wt% NaCl solution and wash it with deionized water. The positive electrode chamber is filled with positive electrode electrolyte; the negative electrode chamber is filled with negative electrode electrolyte, and a peristaltic pump is used through a silicone tube pipeline connected to the inlet and outlet of the negative electrode chamber of the battery, and connected to an external beaker containing negative electrode electrolyte, so that the negative electrode electrolyte is in a flow circulation state; the two sides of the positive electrode chamber are the negative electrode chamber and the air chamber respectively. The positive and negative electrode electrolytes are isolated by an ion exchange membrane to avoid direct contact. The key materials obtained in steps 1), 2), 4), and 5) are assembled into a battery for testing, and the positive and negative electrode current collectors are stainless steel strips and nickel-plated steel strips respectively.
电流测试:用武汉蓝电电池测试系统从5mA至70mA,每隔5mA连续恒流放电10s,并每间隔2s测量开路电压。Current test: Use Wuhan Blue Electric Battery Test System to discharge continuously at a constant current of 5 mA to 70 mA for 10 seconds, and measure the open circuit voltage every 2 seconds.
本实施例中,所形成的电池体系能够稳定处理模拟实际工业生产的废酸废碱溶液。由图4极化曲线可知,在输出电流稳定在40mA时,电池的输出功率最大,达到22mW。In this embodiment, the battery system formed can stably treat waste acid and waste alkali solutions simulating actual industrial production. From the polarization curve in Figure 4, it can be seen that when the output current is stabilized at 40mA, the output power of the battery is the maximum, reaching 22mW.
表1Table 1
表2Table 2
所述的空气电极的催化剂为铂碳混合物。The catalyst of the air electrode is a platinum-carbon mixture.
所述的负极氢化物活性材料为AB5型镧(La)镍(Ni)合金系中的LaNi5。The negative electrode hydride active material is LaNi5 in the AB5 type lanthanum (La) nickel (Ni) alloy system.
所述的隔膜材料为阴离子交换膜或阳离子交换膜。The membrane material is an anion exchange membrane or a cation exchange membrane.
经过具体实际实验,本发明所形成的电化学电池装置实际开路电压测定值高于1.6伏。该装置每产出87.5毫安时电量,至少有0.15-0.21M的氢离子或者氢氧根离子浓度降幅,处理后的废液酸碱性明显减弱。可见本发明具备高效同步处理废酸废碱并利用处理过程中产生的电量的新功能,利于提高资源化利用率。另外,处理酸性废液和碱性废液时的电量回收率可高达94%,且达到最大功率时(即93mW),电压仍能够维持在1伏左右。反应过程中无废气或废液生成,说明目标反应的选择性高,具有绿色无污染的特点,并提高了资源化利用率。After specific practical experiments, the actual open circuit voltage measurement value of the electrochemical battery device formed by the present invention is higher than 1.6 volts. For every 87.5 milliampere-hours of electricity produced by the device, there is at least a 0.15-0.21M drop in the concentration of hydrogen ions or hydroxide ions, and the acidity and alkalinity of the treated waste liquid are significantly weakened. It can be seen that the present invention has a new function of efficiently and simultaneously treating waste acid and waste alkali and utilizing the electricity generated during the treatment process, which is beneficial to improving resource utilization. In addition, the electricity recovery rate when treating acidic waste liquid and alkaline waste liquid can be as high as 94%, and when the maximum power is reached (i.e. 93mW), the voltage can still be maintained at about 1 volt. No waste gas or waste liquid is generated during the reaction, indicating that the target reaction has high selectivity, is green and pollution-free, and improves resource utilization.
与现有技术相比,本发明技术效果包括:第一,引入金属氢化物作为负极,极大地提升电池实际同步处理工作的安全性与稳定性。第二,电池能从电化学中和的废酸废碱中获取高达94%的电量回收率。第三,基于两腔室及酸碱电极配对的电池结构设计改进,该电池装置可针对性地处理多种不同pH值的废液,提供一种“无害化、减量化和资源化”废酸废碱同步处理技术路径。Compared with the prior art, the technical effects of the present invention include: First, the introduction of metal hydride as the negative electrode greatly improves the safety and stability of the actual simultaneous processing of the battery. Second, the battery can obtain a power recovery rate of up to 94% from the electrochemically neutralized waste acid and waste alkali. Third, based on the improvement of the battery structure design of two chambers and acid-base electrode pairing, the battery device can specifically treat a variety of waste liquids with different pH values, providing a "harmless, reduced and resource-based" waste acid and waste alkali simultaneous treatment technology path.
上述具体实施可由本领域技术人员在不背离本发明原理和宗旨的前提下以不同的方式对其进行局部调整,本发明的保护范围以权利要求书为准且不由上述具体实施所限,在其范围内的各个实现方案均受本发明之约束。The above-mentioned specific implementation can be partially adjusted in different ways by those skilled in the art without departing from the principle and purpose of the present invention. The protection scope of the present invention shall be based on the claims and shall not be limited by the above-mentioned specific implementation. Each implementation scheme within its scope shall be subject to the constraints of the present invention.
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