Source: AQUAMOST, LLC submitted to NRP
A PHOTOELECTROCATALYTIC DEVICE FOR REMOVING AMMONIA FROM WATER
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
0210032
Grant No.
2007-33610-18003
Cumulative Award Amt.
(N/A)
Proposal No.
2007-00408
Multistate No.
(N/A)
Project Start Date
Jun 1, 2007
Project End Date
Jan 31, 2008
Grant Year
2007
Program Code
[8.7]- (N/A)
Recipient Organization
AQUAMOST, LLC
1202 ANN STREET
MADISON,WI 53713
Performing Department
(N/A)
Non Technical Summary
Fish are very susceptible to ammonia toxicity. Ammonia concentrations as low as 0.025 mg/L can kill sensitive species, and even robust fish species can be killed by ammonia concentrations as low as 0.2 to 0.5 mg/L. Nitrate is considerably less toxic to fish, although it too can have negative impacts on fish health at levels of 40-50 mg/L. This sensitivity of fish to nitrogen toxicity limits the expansion of a sustainable aquaculture industry that relies on water recirculation technology for year-round production of fish under controlled conditions and requires little water and land, discharges minimal effluents, and can be set up in cities close to major markets. At present, however, it is more economical to produce food fish in ponds. Photoelectrocatalytic (PEC) oxidation is an efficient and economical solution to the problem of nitrogenous waste removal from water. Recent studies show that ammonia and nitrite can be rapidly oxidized by PEC directly into nitrogen gas. The process uses little energy, produces few if any secondary metabolites such as chlorine, and should be economical to manufacture and operate. These Phase 1 studies will allow us to characterize and optimize the performance of bench-top PEC systems and provide the basis for further development of flow-through commercial units that employ this technology.
Animal Health Component
100%
Research Effort Categories
Basic
(N/A)
Applied
100%
Developmental
(N/A)
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
1020210200070%
3063719102030%
Goals / Objectives
The overall aim of the project is to develop and commercialize a photoelectrocatalytic (PEC) oxidizer for removing ammonia from water that can be easily utilized in aquariums and aquaculture. Preliminary studies have demonstrated that ammonia can be converted by photoelectrocatalysis directly into nitrogen gas. Phase 1 feasibility studies will focus on increasing the rate and efficiency of this reaction. The specific aims in Phase 1 are to evaluate and optimize the following parameters to create the most efficient PEC device for oxidizing ammonia: 1. The chemistry and synthesis of the nanoporous TiO2 photocatalyst (e.g., firing temperature, metal doping, and TiO2 thickness); 2. The applied potential (e.g., 0.3, 0.6, 0.9, and 1.2 VDC); 3. Different UV light sources (e.g., germicidal UVC wavelengths and black-light UVA wavelengths); 4. The initial concentration of dissolved ammonia (e.g., 50, 500, 1000, and 5000 ppb as ammonium ions); 5. Water pH (e.g., 6, 7, 8 and 9); 6. Ionic strength as dissolved sea salt concentrations (e.g., 0, 2, 10 and 35 ppt sea salt); and 7. Alkaline buffers (sodium and potassium bicarbonate, and sodium and potassium hydroxide). In addition, we will fabricate and test at least one prototype flow-through reactor to evaluate the effect of water flow rate.
Project Methods
The core of the technology is a conductive metal electrode (anode) coated with a 200-500 nm thick layer of titanium dioxide (TiO2) photocatalyst. When the photocatalyst is illuminated by near-UV light, highly reactive electrons and holes are generated that promote the oxidation of compounds on the anode surface. Photocatalytic efficiency is improved by applying a positive potential ("bias") across the photoanode to decrease the recombination rate of photogenerated electrons and holes. Depositing metals such as platinum (Pt) or gold (Au) on the surface of the TiO2 can enhance the photocatalytic activity of the TiO2 and change the distribution of reaction products. Most tests will be conducted using static bench-top reactors to rapidly evaluate the effect of the variables described above on reaction kinetics. This approach should generate the most data in the least amount of time and allow us to identify conditions that maximize the efficiency of this process. Since commercial applications will use flow-through reactors, we will fabricate and test at least one flow-through prototype in Phase 1. All bench-top tests will be performed with a three-electrode configuration (anode, cathode and reference electrode) in which the potential on the photoanode will be held constant relative to a saturated calomel reference electrode by a potentiostat connected to the reference electrode through a salt bridge placed close to the photoanode. The current passing through the system will be measured and recorded during all experiments. Standard conditions for most tests will be: pH 7; 1.2 V applied voltage; 5 ppm initial ammonia concentration; germicidal UV light source; no sea salt. The standard photoanode will be prepared with three coatings of TiO2 and fired at 300C. These conditions will be modified as needed for specific tests. Ammonium and nitrite will be added to the water at desired starting concentrations. Tests will begin by applying a potential and illuminating the photoanode. Controls will be conducted with no light and no potential. Subsamples of water will be withdrawn from the reactor at selected times until all ammonia is eliminated from the system (2-3 hrs in preliminary studies). All samples will be analyzed for ammonia, nitrite, nitrate, and pH. The fate of oxidized ammonia will be estimated by mass balance (i.e., if the disappearance of ammonia is not accounted for by the production of nitrite and nitrate, the conclusion is that the ammonia was converted into nitrogen gas). All experiments will be repeated at least three times to ensure statistical validity. The effectiveness of a particular test will be quantified as the rate of ammonia removal from water expressed as a rate constant. By comparing rate constants for reactions performed under different conditions, we can determine conditions that have the greatest effect on photoelectrocatalytic activity, which in turn will allow us to design the most effective and economical devices for specific applications.

Progress 06/01/07 to 01/31/08

Outputs
OUTPUTS: The overall objective of this Phase I project was to verify in the laboratory that photoelectrocatalytic oxidation (PECO) could convert dissolved ammonia primarily into nitrogen gas at rates that were high enough for possible commercial applications in aquaculture. Numerous bench-scale tests in 250-mL batch reactors were performed to evaluate the effects of varying several reaction parameters on the rate of ammonia conversion and the distribution of products. Positive results from these tests resulted in the fabrication of several flow-through recirculating reactors. These model reactors are being evaluated for their performance in small-scale aquariums (up to 10 gallons in size). Initial results of this project were presented by Dr. Terence Barry at the Feb. 2008 meeting of the World Aquaculture Society (WAS) in Orlando, FL. These results were included in a provisional patent application that was submitted before the WAS meeting and will be described in more detail in an upcoming publication. To date, AquaMost has generated considerable interest in the local investment community and has been requested to test its technology for an application involving the treatment of wastewater by a relatively small but well-established company working in this area. In addition, AquaMost has submitted a Phase II SBIR proposal that would extend this research to testing prototype devices with live fish. PARTICIPANTS: Three co-founders of AquaMost played active roles in conducting the Phase I SBIR studies. Walter Zeltner, Ph.D., a physical chemist, served as the Principal Investigator. Terence Barry, Ph.D., an aquaculturist, advised on applications of the technology as it impacts fish and coordinated most day-to-day studies. Dean Tompkins, Ph.D., a mechanical engineer, oversaw device design and fabrication. The co-founders were assisted by two undergraduate students, Mr. Timothy Barry and Mr. Ramsey Kropp, who performed many of the tests and assays required for this project. Their input and suggestions proved quite helpful for the successful outcome of this project. The project included a subcontract with Prof. Marc Anderson at the University of Wisconsin - Madison that provided access to specialty electrochemical characterization instrumentation and technical assistance. In particular, one of Prof. Anderson's M.S. students, Mr. Greg Pepping, assisted on this project by performing some parallel experiments using a different test system and by coordinating measurements of the concentrations of nitrite and nitrate ions produced during the reactions. Results of his studies are being prepared for publication. TARGET AUDIENCES: The technology that was studied for this project involves the physical-chemical conversion of dissolved ammonia directly to nitrogen gas. Successful implementation of this technology would impact a variety of industries and individuals who use the products of those industries. Such industries include home aquariums, recirculation aquaculture, backyard ponds, public aquariums and zoos, zebrafish rearing systems for research, swimming pools and spas, wastewater treatment, and drinking water purification. If this technology can be applied to high concentrations of ammonia, it may also prove useful for a novel water desalination approach under investigation by other researchers.

Impacts
Four key variables were found to have the greatest effect on catalytic activity: the firing temperature of the photoanode, the applied voltage, light irradiance, and water salinity. Other variables tested including pH, initial ammonia concentration, and metallization of the anode had little or no effect on catalytic activity. When the key variables were optimized to provide the fastest ammonia removal rates, no nitrite was formed and less than 15% of the ammonia was converted to nitrate. Therefore, it appears that over 85% of the ammonia was oxidized directly to nitrogen gas. The catalytic activity was affected significantly by the temperature at which the photoanode was heated. This observation suggests that the crystalline structure of the active catalytic material has an important impact on its performance and indicates the importance of optimizing this parameter for whatever grade of titanium is employed for the electrode. As expected, ammonia removal was directly proportional to applied voltage over a wide range of voltages. The rate of ammonia removal is much faster (6 to 10-fold faster) in seawater than in freshwater. Using a 9-watt flow-through prototype, we observed complete ammonia removal (initial conc. 0.6 mg/L) from 7 liters of seawater in 90 minutes. Less than 10% of this ammonia formed nitrate, and no nitrite was detected. The conclusion is that ~90% of the ammonia was converted into nitrogen gas. Further studies using live fish with flow-through reactors will be the focus of our Phase II investigations, although initial studies with fish have gone well and suggest that this technology can provide a viable replacement for biofilters. As expected, the studies performed during Phase I have indicated additional issues that must be addressed in commercializing this technology. Such issues include optimizing electrode geometry and sourcing a relatively inexpensive but effective grade of titanium. However, because results of these studies have been quite positive overall, AquaMost continues to pursue commercialization of this technology.

Publications

  • Barry, T., Zeltner, W., Tompkins, D., Kropp, R., Barry, T., Pepping, G., and Anderson, M. (2008). Photoelectrocatalytic device that removes ammonia from water. Aquaculture Engineering (in preparation).
  • Pepping, G., Anderson, M., Barry, T. (2008) Photoelectrocatalytic oxidation of ammonia/ammonium using TiO2-coated Ti photoanode. Environmental Science and Technology (in preparation).