Source: PANI CLEAN INC submitted to
A HYBRID ELECTRODIALYSIS/ELECTROLYSIS UNIT FOR COMBINED NITRATE REMOVAL AND CONVERSION FROM AGRICULTURAL WASTEWATER
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
1024736
Grant No.
2020-39410-33275
Cumulative Award Amt.
$650,000.00
Proposal No.
2020-06707
Multistate No.
(N/A)
Project Start Date
Sep 1, 2020
Project End Date
Aug 31, 2023
Grant Year
2020
Program Code
[8.4]- Air, Water and Soils
Recipient Organization
PANI CLEAN INC
2350 FLINTSHIRE VIEW
CORALVILLE,IA 522413609
Performing Department
(N/A)
Non Technical Summary
Nitrate is currently the most prevalent groundwater pollutant in Northern America, primarily from agricultural activities and changing nitrogen input to the land surface. In the US, over 7 million Americans drink water from community water systems (CWS) that contain nitrate (NO3-) at concentrations exceeding the maximum contaminant level (MCL). The go-to technologies for nitrate treatment from CWSs produce highly concentrated nitrate brine residuals and are limited by expensive brine disposal and management options.Further, there exist more than 35 million acres of sub-surface drained land in the US and no technology has established a significant market share that removes nitrate from agricultural drainage. Based on the scale of nitrate contamination in community water systems and the growing need to reduce nitrogen load from tile-drainage, the total addressable market for removal of nitrate is sizable.The main technical objective is to demonstrate/validate a highly efficient denitrification unit to treat agricultural return flow at a cost lower than for incumbent technologies. In Phase I, the team developed materials and systems with superior nitrate removal and conversion efficiencieswhen compared to IX, RO, and bioreactors. In Phase II, downselected Phase I materials and systems will undergo extensive optimization, testing, and operation in lab-scale and industrial-scale prototypes to reach nitrate removal efficiencies exceeding 95% and stability exceeding 1000 hours in accelerated testing conditions. To reach these objectives, the team will synthesize novel catalysts with tunable physical and chemical composition, will develop novel spectroscopic techniques to investigate its corrosion mechanism, test them in lab-scale and industrial-scale relevant reactors and perform a full-fledged technoeconomic analysis to identify pathways for the commercialization. At the end of Phase II, Pani Clean Inc will have a small engineering scale nitrate treatment unit with nitrate conversion efficiencies exceeding 95%, freshwater recovery percentages exceeding 95%, no brine disposal issues, and cost less than $1.2 per 1000 gallons of treated water a four to fivefold decrease compared to incumbent technologies.The 1,706 community water systems (CWS) experiencing recent violations of nitrate levels primarily from agricultural practices represent the immediately addressable market. The near-term application would be to treat nitrates at the edge-of-field and as POU nitrate treatment systems for individual residences with nitrate contaminated private wells.
Animal Health Component
40%
Research Effort Categories
Basic
25%
Applied
40%
Developmental
35%
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
11102102020100%
Knowledge Area
111 - Conservation and Efficient Use of Water;

Subject Of Investigation
0210 - Water resources;

Field Of Science
2020 - Engineering;
Goals / Objectives
The main goal of this project is to demonstrate and validate a highly efficient denitrification unit to treat agricultural return flow at a cost lower than for incumbent technologies. In Phase I, the team developed materials and systems with superior nitrate removal and conversion efficiencies (>80%) when compared to ion exchange, reverse osmosis, and bioreactors. In Phase II, downselected Phase I materials and systems will undergo extensive optimization, testing, and operation in lab-scale and industrial-scale prototypes to reach nitrate removal efficiencies exceeding 95% and stability exceeding 1000 hours in accelerated testing conditions.The specific objectives to achieve this goal include:(i) Synthesize cost-effectivecatalytic materials and demonstrate improved performance for nitrate reduction compared to catalysts synthesized in Phase I;(ii)Investigate potential-dependent corrosion tolerance of the catalyst using electroanalytical and spectroscopy tools and optimize catalyst formulations based on the results;(iii) Testing of the synthesized catalystsfor their nitrate conversion efficiency, freshwater recovery, and durabilityfor continuous removal and conversion of nitrates in different feed water sources in lab-scale and industrial-scale relevant reactors; and(iv) Performing a full-fledged techno-economic analysis to identify pathways for commercialization.
Project Methods
The scientific methods build upon team strengths in the design and synthesis of functional materials, experimental and analytical electrochemistry, and advanced water treatment processes. Specifically:Catalyst synthesis:Two unique electrodeposition methods will be explored for catalyst synthesis. In the first, the multi-metal alloy catalyst will be deposited using a single bath using a modified pulseelectrodeposition technique. In the second method, we will first deposit multi-metal alloy catalystsusing pulse electrodeposition and chemical reduction techniques. All synthesized catalysts will be characterized for their morphology and elemental composition using high angle annular dark field-scanning transmission electron microscopy and energy dispersive X-ray analysis (EDX). X-ray photoelectron spectroscopy (XPS) will be used to probe their local electronic structure and their interaction with the support material. Catalyst loading will be determined using inductively coupled plasma atomic emission spectroscopy (ICP-AES). Electrochemically active surface area (ECSA) will be determined using electrochemical impedance spectroscopy (EIS) by measuring its double-layer capacitance. Total Surface area measurements will be measured using an automated multipoint BET apparatus.Electrochemical characterization of catalyst for nitrate reduction in batch mode:The synthesized catalysts we will use an in-house two-compartment electrochemical beaker cell for initial screening of catalyst activity and durability. The beaker cell allows for rapid and cost-effective screening of catalytic activity in batch mode. The catalyst activity and durability will be investigated using potential cycling techniques andby performing constant-potential electrolysis for a range of potentials for 1-2 hours with headspace continuously purged into the sampling loop of a gas chromatograph for gas-phase products quantification. The liquid products will be quantified using Nuclear Magnetic Resonance spectroscopy and high-performance liquid chromatography. Besides constant-potential electrolysis, cyclic voltammograms and linear polarization (Tafel slope) will be carried out for kinetic investigations.Electrochemical characterization of catalyst for nitrate reduction in continuous mode:The synthesized catalysts will be testedusing a commercially available 5 cm2 electrolyzer for continuous nitrate reduction. A thorough evaluation of the catalysts will be conducted in two-electrode, continuous electrolyzer mode. Cyclic voltammograms and linear polarization will be carried out for kinetic investigations. Product selectivity and catalyst durability will be carried out for extended periods of time (>100 hrs.). The effect of nitrate concentration, pH and temperatureon nitrate reduction will be evaluated.Methods to determine catalyst stability:To investigate the loss in mass activity of the catalyst in-situ, catalyst coated on quartz crystal microbalance (QCM) substrates and decrease in catalyst mass will be probed during potentiodynamic polarization experiments. Catalyst ECSA will be periodically measured to monitor the change in intrinsic catalyst activity as a function of time. ICP-AES will be used to monitor the degradation products of the catalysts. To evaluate long-term tolerance, EIS will be used to monitor changes in charge transfer kinetics and electrochemical double layer as a function of a lifetime.In-situ operando spectroscopy tools will also be usedto understand the mechanism of catalysis, corrosion, and fatigue. Specifically, in-situ and operando Surface Enhanced Raman Spectroscopy (SERS) to determine the corrosion mechanism of the catalyst under operation conditions using a custom-built Raman Cell.Construction and testing of catalysts in mini-industrial scale reactorsWe will first design and build a lab-scale (64 cm2) hybrid electrodialysis/electrolyzer unit for nitrate removal and its subsequent conversion to nitrogen. The experience gained by building, troubleshooting, and running 64 cm2 reactor will then be used to build a mini-industrial scale 1600 cm2 reactor. We will develop preliminary system designs which will include process flow diagrams with all the control logistics, and piping and instrumentation diagrams. Optimal design architectures will then be constructed with capability for integrating 3-D electrodes and membranes, anode and cathode supporting electrolyte feed, nitrate-rich water feed, and purge line for product collection and analysis. Membrane and spacer materials for the unit will be selected from commercially available options (e.g., NEOSEPTA cation and anion exchange membranes; PCCell spacers) that are stable in the selected water chemistries and which were tested in lab cells. Ohmic losses will be minimized by controlling the spacing between the membrane/separator and the electrodes/current collectors. Fabrication of the prototypes will make use of the UI Physics shop. However, outside vendors will be used as needed. A preliminary HAZOP analysis will be performed on the system prototype design. Tests of the flow properties and total cell resistance (as measured by EIS technique) will be measured and used in the design of the mini industrial-scale reactor. The optimized catalyst will be tested in the industrial scale reactor usingusing potential cycling techniques andby performing constant-potential electrolysis for a range of potentials for 1-2 hours with headspace continuously purged into the sampling loop of a gas chromatograph for gas-phase products quantification. The liquid products will be quantified using Nuclear Magnetic Resonance spectroscopy and high-performance liquid chromatography. Besides constant-potential electrolysis, cyclic voltammograms and linear polarization (Tafel slope) will be carried out for kinetic investigations.Techno-economic analysis.A conceptual engineering process model will be designed and TEA will be performed. TEA will incorporate both capital costs and operational costs (pumping, electricity, feedstock, etc.). Capital costs will be estimated US EPA capital cost estimating procedures. The team will work with materials vendors to determine costs for system components and manufacturing. Using the bill-of-materials and manufacturing cost estimates for the system components and installations, a detailed technoeconomic assessment of the system will be performed. The economic assessment will include large-scale system cash flow models and sensitivity evaluations of the system to identify system components and performance metrics with the greatest cost reduction potential.

Progress 09/01/20 to 08/31/23

Outputs
Target Audience:Pani Clean is dedicated to engaging a diverse array of target audiences throughout our project. Our focus is not limited to professionals and organizations in the water treatment sector, such as nitrate treatment facilities and potential Original Equipment Manufacturers (OEMs). We are also dedicated to connecting with wider community segments by establishing networks through direct engagement and by participating in industry events, including the Water Environment Federation's Technical Exhibition and Conference (WEFTEC), The Water Council (TWC), and the Ammonia Energy Association (AEA). Our outreach involves building relationships with potential partners in water technology and collaborating with government entities. A key example of this is our interaction with the local nitrate removal facilities in Nebraska and Iowa, and the Government of India for the Jal Jeevan Mission, particularly in areas like Rajasthan, where nitrate levels in water often exceed 1000 ppm due to heavy fertilization. Additionally, our initiatives specifically target groups that are socially, economically, or educationally disadvantaged. This approach ensures that our solutions are accessible to those most impacted by nitrate pollution, thereby promoting inclusive and effective water treatment strategies. Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided?Two chemical engineering graduate students were part of this project, with one hired full-time to serve as the CTO for Pani Clean. The graduate students involved in this project participated in workshop-type group meetings every week, where students were trained to disseminate their weekly research findings in the form of presentations. They also participate in the Venture School program provided by the John Papajohn Entrepreneurial Center (JPEC) at the University of Iowa. How have the results been disseminated to communities of interest?We have actively engaged with communities significantly affected by nitrate contamination. Our outreach has extended to nitrate treatment facilities, rural areas, users of private wells, and various water-centric organizations like the Community Water Center in California. These efforts aim to enhance public awareness and understanding of nitrate issues and to inform communities about the technologies available for addressing these challenges. Additionally, we emphasize the potential for cost-effective solutions, such as converting nitrates into ammonia at a low cost. Our goal is not only to mitigate the impact of nitrates but also to spark interest in science, technology, and the humanities, especially among those who might not typically be exposed to such research activities. What do you plan to do during the next reporting period to accomplish the goals? Nothing Reported

Impacts
What was accomplished under these goals? (i) Synthesize cost-effectivecatalytic materials and demonstrate improved performance for nitrate reduction compared to catalysts synthesized in Phase I; Task 1: Synthesize and characterize metal alloy catalysts with varying Pd content During the initial phase of the project, our research team experimented with a metal alloy deposited on a carbon electrode substrate. This combination proved effective in reducing nitrate pollution in water. However, a significant challenge was the high cost due to the substantial amount of novel metal used. A preliminary technoeconomic assessment revealed that reducing the novel metal content to less than 0.125 mg per square centimeter could maintain performance while achieving a cost reduction of over 30%. This would lower the capital expenditure from $1.36 to $0.89 for every 1,000 gallons of treated water. In Phase II, ourteam discovered that using metal content on a three-dimensional metal electrode substrate was as effective for nitrate reduction as the previous alloy systems on carbon electrodes. By switching to a newer metal system on metal electrodes, the need for costly novel metal was eliminated without compromising performance in nitrate reduction. Our team experimented with different deposition strategies and found the most optimal catalyst deposition parameters based on nitrate reduction performance. Comparisons were made between the catalyst deposits on metal electrodes and those on carbon electrodes. The metal-on-metal electrode displayed a superior ability to reduce nitrates, achieving a higher rate of nitrate reduction and nearly 100% current efficiency. Additionally, the durability of the metal-on-metal electrodes was tested over approximately 100 hours of operation with the efficiency increased after this prolonged use. This research successfully met its key objectives. Reducing the novel metal content to less than 0.125 mg/cm2. and demonstrating over 90% efficiency in nitrate reduction and maintaining stable catalytic activity after 100 hours of operation. The shift to the optimized metallic system proved to be a significant advancement in reducing nitrate pollution in water, offering both economic and environmental benefits. Task 2: Nitrate reduction in a continuous mode using a small-scale commercial electrolyzer The main objective of this part of the project was to test the selected catalysts from an earlier task using a commercially available small-scale electrolyzer. This was done to understand how fluids move through the system and to identify any electrical inefficiencies. This information would help design larger and more efficient electrolyzers in a future task. However, due to delays caused by COVID-19, the team could not get the small electrolyzer initially planned to use.During this delay, our team creatively adapted a larger, 64-square-centimeter unit andproved successful. We were able to continuously reduce nitrate pollution in water, converting over 90% of the nitrates into ammonia and nitrogen. Importantly, more than 70% of the converted nitrates turned into ammonia, showing that the adapted system worked very efficiently. (ii)Investigate potential-dependent corrosion tolerance of the catalyst using electroanalytical and spectroscopy tools and optimize catalyst formulations based on the results; Task 3: Examine loss in catalyst activity using in situ electrochemical approaches Task 4: Examine reaction intermediates to determine corrosion mechanism and product selectivity using in situ operando spectroscopic technique The project involved using an advanced spectroscopy tool for tasks 3 and 4, which is atechniqueto study materials by observing how they interact with light.The aim was to identify certain molecules and reaction stages on the catalyst surfaces when electricity was applied. By doing this, we were able to identifythe exact reaction mechanisms and how the products varied under different conditions. Especially on the mechanism of nitrates converting into nitrogen or ammonia and the certain intermediate stages in the nitrate reduction process. These stagesindicate how the catalyst preferred to convert nitrates either into nitrogen or ammonia.This information is crucial in evaluating the efficiency of the catalysts and how they perform under different conditions. (iii) Testing of the synthesized catalystsfor their nitrate conversion efficiency, freshwater recovery, and durabilityfor continuous removal and conversion of nitrates in different feed water sources in lab-scale and industrial-scale relevant reactors; and Task 5: Design and construct lab-scale and mini-industrial scale hybrid ED/EL unit This task involved creating a small laboratory-sized unit, specifically designed for removing nitrate pollution from water and converting it into nitrogen gas. This unit had an area of 64 square centimeters and was used for carrying out the initial tests in task 2. The knowledge and experience gained from designing, building, and operating this small reactor were crucial. We planned to use this experience to construct a much larger, mini-industrial scale reactor with an area of 1600 square centimeters, more suitable for practical, real-world applications. As for the results, ourteam was successful in building the smaller 64-square-centimeter reactor. This reactor was capable of integrating complex components like three-dimensional electrodes, membranes for separation, and lines for feeding in electrolyte and nitrate-rich water. It also had a special setup for collecting and analyzing the end products. The insights and learnings from this smaller reactor were then used to redesign and construct the larger 1600-square-centimeter reactor. Task 6: Performance evaluation of the lab and industrial scale ED/EL cell for nitrate removal in different feed waters Our team worked on improving a process to remove nitrates from water, using the best catalyst they had developed earlier. We tested this catalyst on large electrodes and integrated it into a laboratory-scale unit designed for both electrodialysisand electrolysis. We first tried this in a small, 64 square-centimeter reactor with water containing high levels of nitrates. The results were promising and managed to remove over 99% of the nitrates in just over an hour for nitrates in all ranges of 20~164 ppm. In the larger unit, 1600 square centimeter reactor, we achieved more than 90% nitrate removal in only 5 minutes for the same nitrate levels tested in the small unit. The >90% conversion was observed for continuous 2 hours of operations. Further tests were done using waters that simulated real water chemistries. The system performed well in these tests, with no decrease in nitrate removal or conversion rates. An actual brine sample from the nitrate treatment facility in Hastings, NE, was tested and we achieved over 90% efficiency in both removing nitrates and converting a significant portion into ammonia. An important part of this project was to design the system ensuring the feasibility of fitting all components within a consumer-acceptable form factor. The design includes all necessary parts: the combined electrodialysis/electrolysis unit, tanks for storing clean and contaminated water, pumps, valves, flow meters, and pressure gauges. The design was translated into a real, functional unit. This unit was connected to a solar-powered console, making the entire operation run on solar energy. iv) Performing a full-fledged techno-economic analysis to identify pathways for commercialization. Task7: Technoeconomic analysis An extensive techno-economic analysis was conducted to explore ways to reduce the cost of metal-on-metal electrodes and to assess the economic viability of producing ammonia from nitrates. This involved calculating the leveled cost of ammonia (LCOA) generated from water contaminated with various concentrations of nitrates.

Publications


    Progress 09/01/21 to 08/31/22

    Outputs
    Target Audience:Pani Clean has been continuing its efforts as reported in Year 1 of this grant, including forming networks with potential OEM and contract manufacturers by directly contacting the companies or visiting their exhibit booths at the Water Environment Federation's Technical Exhibition and Conference (WEFTEC). Pani Clean has also been working with Larta consultants to identify the immediate market segments. Additionally, Pani Clean has soformed good relationships with Partners from consultant companies in MENA regionwith expertisein management consulting and water technologies to establishpartnerships and possible Joint ventures in the region. Changes/Problems:Due to COVID, we had delays starting with Task2 which had a trickle effect completing all our tasks in two years. We have asked for a no-cost extension to complete the remaining (50%) of Task 6 and Task 7. What opportunities for training and professional development has the project provided?Silimar to year 1,two chemical engineering graduate students were part of this proposal, with one hired full time to serve as CTO for Pani Clean. The graduate students involved in this project participated in workshop-type group meetings every week, where students were trained to disseminate their weekly research findings in a form of presentations. How have the results been disseminated to communities of interest?One paper on theoperando spectroscopy to monitor nitrate reaction products is being revised for submission. What do you plan to do during the next reporting period to accomplish the goals?We have asked a no-cost extension to complete Task6 and Task 7. In Task 6,we will demonstrate mini-industrial scale ED/EL unit for continuous nitrate removal and conversion and evaluate its performance metrics. In Task 7,we will conclude TEA modeling with a sensitivity analysis to clarify necessary cost/performance metrics to commercialize this process

    Impacts
    What was accomplished under these goals? This project had 7 R&D tasks spread across 2 years. In year 1,we completed Tasks 1, 4 and 5. In this project report, we accomplushed Task 2, Task 3, completed 50% of Task 6 and Task 7. Task 2:In this task, we proposed to assemble and test 5 cm2 electrodes in continuous electrolyzer mode using catalysts prepared through Tasks 1 and evaluate their performance and durability for nitrate conversion in model nitrate-rich waters. A 5 cm2 (active electrode area) electrolyzer was built and re-engineered to perform nitrate reduction in a continuous mode. We perofrmed electrochemical evaluation, includingpolarization curves as a function of nitrate concentration, constant potential and constant current eletrolysis, and investigated product distribution ratios as a function of potential and time. We also investigated the effect of catalyst/substrate interaction on product selectivity and current yield. Task 3: In this task, the goal was to examine the loss in mass and intrinsic activity of the catalyst using in situ electrochemical approaches. We performed electrochemical active surface area measurements of the catalyst as a function of operational time and observed no changes to the intrinsic activity of the catalyst or drop in surface area. The ICP measurements did not show any loss of catalyst mass after continuous operation of the catalyst in model-nitrate waters. Task 6: In this task, the goal was to evaluate lab and mini-industrial scale ED/EL cell for nitrate removal in different feed waters. The best-in-class nitrate reduction catalyst was integrated to lab and mini-industrial scale ED/EL unit. The overall goal here was to understand the effect of system size on nitrate treatment performance for wider market adoption. The effect of water composition and nitrate concentration on the ED/EL unit performance was investigated. Different feed water chemistries were selected based on the US brackish water data published by the Department of Interior.We completed assessment of the nitrate removal and conversion in different feed water chemistries for lab scale unit. We are currently working on assesing the nitrate removal and conversion efficacy in industrial scale unit. We have requested a no-cost extension for completing Task 6. Task 7: In this task, the goal was to complete the technoeconomic analysis using the data derived from the Tasks 2, 5, and 6. We designed a conceptual engineering process model to performTEA for three commercial applications: (1) To treat nitrate-rich tile drainage; (ii) To treat nitrate contaminated community water systems ; (iii) Nitrate treatment for POU application. We are currently gathering relevant data from Task 6 which will then serve as input for Task 7.We have requested a no-cost extension for completing Task 7.

    Publications


      Progress 09/01/20 to 08/31/21

      Outputs
      Target Audience:Pani Clean has contacted various end customers and customer-facing entities by participating in the NSF I-CORPS program. We achieved over 110 interviews with end-users (farmers, well owners), water facility managers, large corporate managers, etc. This has given us a good understanding of the product requirements for potential users - cheap, easy operation, and low maintenance should be met to have a viable product. Our consultant in Larta is also proactively assisting the process by offering suggestions for exhibitions, conferences, and regulators to reach out for collecting helpful information on the product requirements. Pani Clean has actively been forming networks with potential OEM and contract manufacturers by directly contacting the companies or visiting their exhibit booths at the Water Environment Federation's Technical Exhibition and Conference (WEFTEC). We formed good relationships with potential OEM partners such as Snow Pure technologies, and contract manufacturers. Changes/Problems:For this interim report, the goals were to complete R&D Tasks 1 and 2 and to initiate Task 5. However, due to COVID-19, there were delays with procuring the commercial electrolyzer needed for Task 2 and we were unable to complete it by the end of Year 1. We currently have the commercial electrolyzer and anticipate completing Task 2 by the end of Q1 Year 2. However, during this downtime, we worked on Tasks 4, 5, and 6. We completed Task 4 and Task 5 which had initially planned date of completion during Year 2. What opportunities for training and professional development has the project provided?Two chemical engineering graduate students are part of this proposal, with one hired as a research intern for Pani Clean. The graduate students involved in this project participated in workshop-type group meetings every week, where students were trained to disseminate their weekly research findings in a form of presentations. How have the results been disseminated to communities of interest?Two manuscripts - one on the application of operando spectroscopy to monitor nitrate reaction products and the other on the initial proof of concept on the hybrid ED/EL unit for nitrate capture and conversion - are in preparation for publication in peer-reviewed journals What do you plan to do during the next reporting period to accomplish the goals?In the next reporting period, we aim to complete testing the catalyst in a commercial small-scale electrolyzer and apply the best-in-class catalyst to demonstrate the hybrid ED/EL process in a mini-industrial scale unit. We will also complete a preliminary technoeconomic analysis for our process. For the mini-industrial scale reactor, we will evaluate the effect of feed water chemistries on nitrate capture and conversion efficiencies.

      Impacts
      What was accomplished under these goals? Task 1: Synthesis and performance characterization ofthe proprietary catalyst using a batch reactor. While the focus of the task was to reduce the noble metal content in the proprietary alloy catalyst, we serendipitously discovered that an earth-abundant catalyst deposited on high surface area metal support can achieve nitrate conversion with selectivity >95%, far exceeding our prior reports. These catalysts when tested in a beaker cell showed no degradation for nitrate conversion after 100 hours of operation. Thus, achieving all proposed milestones for this task. Task 2: Nitrate reduction in a continuous mode using a commercialelectrolyzer. In this task, we proposed to reengineer a commercially availablewater electrolyzer for continuous nitrate reduction studies. However, due to COVID-19, we had a delay with the purchase of the commercial electrolyzer unit. We recently acquired the electrolyzer unit and are in the process of reengineering the design to test the activity, selectivity, and durability of the catalysts identified from Task 1 in continuous mode. Task 4: Examine reaction intermediates to determine product selectivity using in situ operando technique. This task was initially designed to be carried out in year 2 but was moved to year 1 to make up for the electrolyzer downtime in Task 2. Using in-situ and operandospectroscopywe determined the reaction intermediates on catalyst surfaces under operation conditions. Notably, we observed that different electrochemical voltages yielded different surface adsorbates with catalyst favoring nitrogen and ammonia formation when operated at large overpotentials and nitrite at low overpotentials. The above finding illustrates that by careful tuning of the applied potential, the same catalyst can be tailored to yield different nitrate reduction products. We successfully achieved the milestone associated with this task. Task 5: Design and construct a large lab-scale hybrid ED/EL unit. In this task, we first designed and built a large lab-scalehybrid electrodialysis/electrolyzer unit for nitrate removal and its subsequent conversion to nitrogen. The experience gained by building, troubleshooting, and running a large lab-scalereactor will then be used to build a mini-industrial scale reactor. The large lab-scalereactor was successfully constructed with the capability for integrating proprietary electrodes and catalysts with electrolyte feed, nitrate-rich water feed, and purge line for product collection and analysis. A preliminary HAZOP analysis was also performed on the system design. Tests of the flow properties and total cell resistancewere measured with total cell resistance <10 Ohm cm2. Thereby, successfully achieving Milestone 6. Task 6: Performance evaluation of the lab-scale ED/EL cell for nitrate removal in different feed waters. This task, like Tasks 4 and 5 was started earlier to make up for the electrolyzer downtime in Task 2. The best-in-class nitrate reduction catalyst was deposited on large area proprietaryelectrodesand integrated into a lab-scale ED/EL unit. The integrated electrodes were then first tested to evaluate their performance in model nitrate-rich waters. We successfully were able to recover >95% nitrate from nitrate-rich waters and were able to convert >60% of them. We are currently optimizing the catalyst loading for the lab-scale unit to achieve >90% nitrate conversion in model nitrate-rich water and in waters that simulates real water chemistries.

      Publications