Innovative Photoelectrocatalytic filter for Recirculating Aquaculture Systems

Introduction and Motivations Ammonia poses a threat to biodiversity in aquatic environments, having toxic effects on fish and animals living in freshwater and seawater1. Land-based aquaculture uses recirculating aquaculture systems, which take advantage of biological filters to oxidise ammonia to nitrite ion NO2 - and the much less toxic nitrate ion NO3 -. Periodical replacement of water leads to the emission in the environment of large amounts of nitrogen rich wastewater, contributing to eutrophication in fresh and seawater. It’s possible to couple a semiconductor to the already present Hg-UV lamp setups in fish farming plants, to construct a photoelectrochemical reactor which exploits the UV-electrochlorine advanced oxidation process. The semiconductor coated anode illuminated by the lamp oxidizes chloride ions naturally present in fresh- (or sea-) water, the generated highly reactive chlorine species oxidize the ammonia released by fish and convert it into NO3 - and the more inert N2.2 Materials and Methods Synthesis of the photoanode material is achieved through an easily scalable anodization procedure yielding highly active thin film of TiO2 arranged in self-assembled vertical nanotubes arrays from metal Ti metal substrate.3 Ti mesh tubes of 4 cm diameter and 39 cm long are anodized in an electrolyte solution of 0.2 M HF, 8 M H2O in ethylene glycol at 30 V for 1.5-6 h. Finally, the meshes are rinsed and sonicated in absolute ethanol, following calcination at 450°C for 2 h with heating ramp of 10 °C min-1. Preliminary tests were performed in a 1.08 L glass lab scale reactor (fig. 1). A metal Ti mesh tube surrounding the TiO2 coated photoanode is used as counterelectrode, water is recirculated by a rotary pump from a 2.5 L tank. Ammonia degradation tests are run on 5 mmol L-1 KCl and 100 ppm NH3 solutions at 4 V potential bias. Periodical analysis of NH4 +, NO2 - and NO3 - by ion chromatography allows to trace ammonia conversion and selectivity towards the NO2 - and NO3 - N2 products. In vivo tests have been performed with six individual tanks (three control and three treated groups), with a recirculating flow rate set at ca. 120 L/h. A total of 375 g of juvenile rainbow trout (around 60 individuals/tank, 16 SO39 °C, 10 L/14 D photoperiod), at 7.5 kg/m3 density and fed twice daily (0.7% body weight) was distributed in each tank at the beginning of the test. Results and Discussion Anodization of the Ti metal meshes in presence of HF yields a TiO2 thin film layer arranged in a vertical nanotube array as shown in the SEM image in fig. 1. The film composition is anatase, and show very high photoactivity in the UV range at λ < 380 nm. Ammonia concentration linearly decreases overtime while NO2 - accumulates over the first 2 hours and is then further consumed, NO3 - concentration increases during the whole experiment as ammonia is converted. The concentration profiles are typical of consecutive reactions where NO2 - is the first intermediate and is then consumed to make the NO2 - end product. Selectivity toward nitrate only reaches up to 50% of the total ammonia converted, and the remaining nitrogen is converted to N2. Optimization of the synthesis procedure by changing the anodization time from 1.5 h to 6 h allows to increase the photocurrent and increase the overall PEC performance of the reactor. Figure 1 SEM image of the anodized Ti mesh (a), lab-scale PEC setup (b), variation of NH3 (black), NO2 - (green), and NO3 - (blue) concentration (c) and selectivity to NO2 - (green), NO3 - (blue), N2 (red) (d) during the PEC experiment in KCl 5 mM. By contrast, only a slight XNH3 (ca. 10 %) is observed in K2SO4 electrolyte solution. These results suggest that chlorine has