Background

Controlling infectious diseases is one of the main challenges faced by the fish farming industry [1]. A wide range of pathogenic microbes cause a variety of diseases, including furunculosis, infectious pancreatic necrosis, infectious salmon anaemia and amoebic gill disease, each of which results in extensive economic losses [2, 3]. There is a growing awareness of the need to eliminate such pathogens by disinfecting the water in the aquaculture systems [4, 5]. Disinfection is an effective treatment for many types of pathogenic microorganisms, including viruses, bacteria, fungi and protozoan parasites [6]. However, water disinfection remains a scientific and technical challenge [7]. The most commonly used techniques for water disinfection are chlorination, membrane filtration and ozone treatment [8] but antibiotics and biocides have also been used. Unfortunately all have disadvantages, particularly in relation to the generation of toxic by-products which may cause health risks to human consumers [9]. Additionally, some viral vaccines have been developed in the past two decades, but these are limited to selected viral pathogens and they are also extremely costly to produce and to administer [10].

Solar radiation is an alternative, low-cost, effective technology for water disinfection [11]. Solar disinfection normally refers to exposure of contaminated water to natural sunlight for a sufficient length of time to reduce the number of pathogenic microbes below the infective dose [5, 12]. So far the most commonly employed method for solar disinfection is to expose contaminated drinking water kept in transparent plastic containers to full sunlight for at least 6 h [11, 13] which is slow, and is not always feasible as a result of daily and seasonal variations in weather conditions.

Solar disinfection can be enhanced substantially by using certain photocatalysts such as the photoactive semiconductors TiO2, ZnO, Fe2O3, WO3 and CdSe. These photocatalysts produce highly reactive oxygen species (ROS) which destroy microbial pathogens; this is known as solar photocatalytic disinfection [14, 15]. Titanium dioxide (TiO2) is one of the most widely used, stable and active photocatalysts in water disinfection [8]. It has shown its effectiveness not only in small-scale solar disinfection reactors but also in pilot studies of large-scale solar photocatalysis for drinking water and waste water [16–19].

Typically, TiO2 slurries are used for chemical and microbial photodegradation [9, 19]. However, such slurries create problems in separating the photocatalyst from the treated water, leading to the development of reactors containing an immobilised photocatalyst. Different types of solar photocatalytic reactors have been developed for water treatment [20]. The most frequently used types of reactors are: (i) the parabolic trough reactor (PTR), (ii) the double skin sheet reactor (DSSR), (iii) the compound parabolic collecting reactor (CPCR) and (iv) the thin-film fixed-bed reactor (TFFBR). The most important part of a TFFBR is a sloping plate coated with P25 TiO2 DEGUSSA over which flows the contaminated water during use. The TFFBR also contains a pump, by which the water flow rate can be controlled. The main advantages of this TFFBR are (i) its high optical efficiency, (ii) it's simple construction method and (iii) the low investment costs involved in development. Further advantages are that oxygen transfers effectively into the water film and there is no need for TiO2 separation from the treated water, in contrast to reactors based on TiO2 slurries.

An understanding of the mechanism of microbial photoinactivation during solar photocatalysis comes mostly from studies of bacteria [5, 7, 21]. The most common photocatalytic inactivation mechanism described is based on inactivation due to hydroxyl radicals and other reactive oxygen species (ROS) when bacteria come in contact with a solar-excited photosensitiser. This photooxidation process causes cell membrane disruption and increase cellular permeability, with significant cell damage that eventually results in complete inactivation of the bacteria [13].

The conventional approach to assessing the viability of bacteria during solar disinfection is to enumerate samples after exposure to sunlight, using conventional plate counts on a suitable agar-based growth medium with incubation of plates in standard aerobic conditions (e.g. 24 h incubation at a suitable temperature). However, recent studies have demonstrated that reactive oxygen species (ROS), derived mainly from aerobic respiration during the enumeration process, may inactivate sub-lethally damaged bacteria and prevent their growth and enumeration under aerobic conditions [22]. Such injured cells can only be cultured and counted under conditions where reactive oxygen species are neutralised (ROS-neutralised conditions) e.g. by supplementing the growth medium with the peroxide scavenger sodium pyruvate and incubating under anaerobic conditions to prevent cellular respiration, allowing the bacteria to grow by fermentation [22–24]. This approach was taken in the present study; uninjured bacteria were enumerated under aerobic conditions while uninjured plus injured (ROS-sensitive) bacteria were enumerated under ROS-neutralised conditions, with the difference between the counts under both sets of conditions representing the number of injured bacteria in the sample.

Even though bacteria have received more attention than other groups of microbes in solar photocatalysis research, bacterial pathogens of fish have been largely ignored in these studies, prompting the study reported here. Aeromonas hydrophila is a Gram-negative bacterium, known to be a primary fish pathogen [25]. A. hydrophila tends to be virulent towards most cultured and wild freshwater fish, especially trout, salmon, carp, catfish and tilapia. Red fin diseases and haemorrhagic septicaemia are mainly associated with A. hydrophila [26]. Antibiotics and several vaccines have been used to treat these infections, but extensive use of antibacterial agents has caused A.hydrophila to develop resistance towards certain antibiotics including, ampicillin, tetracycline, chloramphenicol and sulphonamides, [27]. Consequently, it is now important to develop alternative treatments for this pathogen.

The present research reports on the development of a system for the disinfection of water contaminated with A. hydrophila ATCC 35654 as a model for solar photocatalysis in aquaculture systems. The result presented here show for the first time that solar photocatalysis can provide an effective means of inactivation of A.hydrophila, which provides proof-of-concept for the application of solar photocatalysis in aquaculture systems.

Methods

Reactor

A pilot-scale thin-film fixed-bed reactor (TFFBR) system has been developed, based on two previous researches [28, 29]. The overall experiment was set-up as a single-pass process and the reactor consisted of a water reservoir (representing an aquaculture pond in the model system), an air-controlled pump, a solar collector (glass plate) with immobilised photocatalyst, P25 TiO2 DEGUSSA and a collector vessel for the treated water (Figure 1). As in previous studies of chemical degradation [28, 29] and recent studies of microbial inactivation [7, 21], the reactor angle was maintained at 20° throughout, and the light intensity was measured from the same angle as that of the reactor. The illuminated surface area was 1.17 m in depth and 0.40 m in width; the irradiated volume was 200 mL in 2.5 min (irradiance time) and the density of the TiO2 photocatalyst 20.50 g m-2 and the photocatalyst layer was not covered during the experiments.

Figure 1
figure 1

(a) schematic diagram and (b) photograph of the thin-film fixed-bed reactor (TFFBR) used in this study.

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The TiO2 P25 Degussa photocatalyst was coated on four pieces of 3.3 mm thick Borofloat 33 glass plates (Schott, Australia). Plates were degreased using a reagent grade Piranha solution (3:1 sulphuric acid and 30% hydrogen peroxide). Then a slurry of TiO2 was prepared with methanol and the glass was coated by spraying. Then it was baked at 450°C for 2 h to anneal the TiO2 to the glass.

Bacterial culture

Aeromonas hydrophila ATCC 35654 was purchased from Oxoid, Australia. This was maintained by repeated sub-culture on trypticase soy agar (TSA) (Oxoid, Australia) at 25°C. The stock cultures were stored at-70°C in sterile saline containing 20% (v/v) glycerol. For experimental use, cultures were prepared by loop inoculation of bacteria into 100 mL of trypticase soy broth (TSB) (Oxoid, Australia) on a shaking water bath for 24 h at 25°C. To obtain a working cell suspension, the overnight culture was centrifuged at 13000 g for 1 min. The supernatant was discarded and the cell pellet was rinsed twice with water prepared by reverse osmosis, to remove all traces of the growth medium. Then 6 mL of this cell suspension was added to the 6 L of sterile natural spring water (Satur8 Pty. Ltd, Australia) to give an initial bacterial count of 105 CFU/ml added to the reservoir of the reactor.

Experimental procedure

For each experiment water containing A.hydrophila ATCC 35654 was run from the reservoir through the reactor for at least 30 min with different flow rates (4.8 L h-1, 8.4 L h-1and 16.8 L h-1) controlled by an air-pressure pump. Every 10 min a water sample was collected in a sterile McCartney bottle from the outflow of the TiO2-coated plate, labelled and returned to the laboratory, shielded from further exposure to sunlight. Reservoir samples were also collected at 0 min and 30 min to provide the untreated (dark) control counts for each experiment. During the experiment, every 2 min, total sunlight intensity readings were obtained in W/m2 using a Pyranometer (model SP1110, Skye instruments, UK). At the same time solar ultra-violet (UV) light intensity readings were also measured using a Solarmeter (model 5.0, UV meters, Solartech, Inc, USA). Experiments were carried out under different sunlight conditions with a range of total sunlight of 300-1200 W m-2 and UV intensities of 20-60 W m-2. A comparative experiment was also carried under full sunlight (> 1000 W m-2) with the same procedure using a glass plate of the same size but without TiO2 in the TFFBR at 4.8 L h-1.

Laboratory enumeration

Each sample was processed by serial decimal dilution to cover the range 100-10-2. Then three aliquots of 20 μL of each dilution were plated by the droplet spread technique [23] on TSA with or without 0.05% w/v sodium pyruvate and incubated at 25°C for 48 h. Plates without sodium pyruvate were incubated in a conventional aerobic incubator (Cotherm, Biocell 1000, Thermo Fisher Scientific Ltd. Australia), to provide counts of healthy bacteria. Plates with sodium pyruvate were incubated under anaerobic condition in a dedicated anaerobic cabinet (Model 10, COY Inc., USA) to create ROS-neutralised conditions, giving the count of healthy bacteria plus injured bacteria. Plates were counted using a colony counter and converted to log10 CFU/mL. To provide a measure of the inactivation that occurred due to solar photocatalysis, the log-transformed count of sunlight-treated water at each time point were subtracted from the log-transformed count of untreated water (dark control) to give an overall value for log inactivation. As an example, for a treated log count of 3.83 and an untreated log count of 5.16, then log inactivation = 5.16-3.83 = 1.33, which represents (antilog 1.33) a reduction in absolute count of around twenty-fold.

Statistical comparisons of different data sets were carried out using regression analysis of log-transformed data.

Results

Effectiveness of TiO2 photocatalyst on inactivation of A. hydrophilainactivation

In Figure 2, spring water with an initial level of 5.16 Log CFU ml-1 Aeromonas hydrophila (ATCC 35654) showed only 0.06 log inactivation with a single pass across the glass plate reactor (no TiO2) with a final average concentration of 5.1 log CFU ml-1 and with no detectable cell injury, under high sunlight intensity of (1032-1187) W m-2 (UV light intensity = 52.8-62.8 W m-2). On the other hand, a single pass across the TFFBR with TiO2 showed 1.33 log inactivation, with minimal cell injury, with an average final concentration of 3.83 Log CFU ml-1 from a similar 5.16 Log CFU ml-1, initial level of A. hydrophila.

Figure 2
figure 2

Effect of TiO 2 photocatalyst on inactivationof A. hydrophila (ATCC 35654) under high sunlight condition (1032-1187) W m-2 or (UV light intensity = 50.8-62.8 W m-2) at 4.8 L h-1, with and without TIO 2 coating on the TFFBR single pass reactor. Enumeration was carried out under standard aerobic conditions (unfilled bars) and under ROS-neutralised condition (filled bars).

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Interrelationship of flow rate and total sunlight on inactivation of Aeromonas hydrophila

Figure 3a shows the log inactivation data for A.hydrophila ATCC 35654 in sterile spring water run through the TFFBR at 4.8 L h-1 flow rate under various total sunlight conditions, from 300 W m-2 to 1200 W m-2, and then enumerated under (i) aerobic and (ii) ROS-neutralised conditions. Thus, each experiment provides two sets of log inactivation data, (i) an aerobic result, based on healthy cells only and (ii) a ROS-neutralised result, representing healthy and injured cells together. At low total sunlight intensities of < 600 W m-2, there was a far larger difference between the log-inactivation values obtained using aerobic and ROS-neutralised counts than was the case for sunlight intensities above 600 W m-2. This demonstrates a far greater proportion of injured (ROS-sensitive) cells at lower sunlight conditions (< 600 W m-2). In contrast, higher sunlight intensities ranging from 600 W m-2 to 1100 W m-2 resulted in greater proportional inactivation (higher log inactivation values), whether quantified both in aerobic or ROS-neutralised conditions, with minimal differences in log inactivation values. This demonstrates that at high sunlight intensities, inactivation is not accompanied by sub-lethal injury, in contrast to the findings at lower sunlight intensities (< 600 W m-2).

Figure 3
figure 3

Effect of different flow rates (a) 4.8 L h-1, (b) 8.4 L h-1 and (c) 16.8 L h-1, on log inactivation of A.hydrophila ATCC 35654 in spring water run through the TFFBR under different total sunlight conditions. Enumeration was aimed at under standard aerobic conditions (open circle) and under ROS-neutralised conditions (closed circle).

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Linear regression trend lines were plotted for each data set (i.e. for log inactivation data obtained from counts under aerobic and ROS-neutralised conditions). ROS-neutralised condition predicted a best fit line with an intercept close to zero and a strong fit of the data to the trend line, based on a regression coefficient of 0.751 (Table 1). In contrast under aerobic conditions, the trend line has a positive intercept and a weaker fit, with a regression coefficient of 0.535. Given that the logical expectation is that there would be no inactivation at 0 W m-2 sunlight, this is consistent with the notion that data based on ROS-neutralised counts provide a more appropriate measure of inactivation than standard aerobic counts, with the latter give a substantial overestimate of the effectiveness of solar photocatalysis at low sunlight intensities (< 600 W m-2).

Table 1 Linear regression analysis for inactivation of A.hydrophila ATCC 35654 under 3 different flow rates
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Figure 3b and 3c showed the log inactivation data for A.hydrophila ATCC 35654 in spring water run through the reactor at flow rates of 8.4 L h-1 and 16.8 L h-1, respectively, under equivalent sunlight conditions to those shown in Figure 3a. Both graphs show a similar pattern of greater proportional cell injury, manifest as ROS-sensitivity and lack of growth under aerobic conditions, to the data for low flow rate (Figure 3a) when the total sunlight intensity was < 600 W m-2. Similarly, when the total sunlight intensity was 600-1100 W m-2, there was a greater log inactivation and less evidence of sub-lethal injury.

Linear regression analyses were also carried out for flow rate data at 8.4 and 16.8 L h-1. At both flow rates, the trend lines based on aerobic counts gave positive intercepts whereas the ROS-neutralised data showed an intercept close to zero, in line with the outcome at 4.8 L h-1 (Table 1). Similarly, the aerobic count data at 8.4 and 16.8 L h-1 had lower regression coefficients than for ROS-neutralised data. Overall, the interpretation of these data is that aerobic counts overestimate the apparent inactivation of A. hydrophila ATCC35654 and that ROS-neutralised counts are required to provide counts of injured and healthy cells, with trend lines that fit with the logic of a zero intercept and a strong fit of the data to the trend line. Based on ROS-neutralised data, there is a strong effect of flow rate on photocatalysis using the TFFBR--this is evident from the decrease in slope for the linear regression analysis based on the ROS-neutralised data from the slowest flow rate (4.8 L h-1) to the fastest flow rate (16.8 L h-1), shown in Table 1. An equivalent change was not observed for aerobic data, which again points to the issues around low aerobic counts at low sunlight intensities and their effects on the overall trend data.

The data in Figure 3 also demonstrate that the combination of a low flow rate of 4.8 L h-1 combined with a total sunlight intensity of 600 W m-2 or more gave the greatest log inactivation of A. hydrophila ATCC 35654, pointing to such conditions as being most effective for solar photocatalysis.

Interrelationship of flow rate and solar UV on inactivation of Aeromonas hydrophila

Figure 4 shows the log inactivation rate of A.hydrophila (ATCC 35654) in spring water run through the reactor with 3 flow rates (4.8, 8.4 and 16.8 L h-1), with the data plotted against solar UV intensity, ranging from 20 W m-2 to 80 W m-2, to see whether the same results were obtained as for total sunlight in Figure 3. This was carried out because TiO2 is specifically photoactivated by UV light at 390-400 nm. Overall, the same trends of (i) positive intercepts for log inactivation data based on aerobic counts (ii) close-to-zero intercepts for log inactivation data based on ROS-neutralised counts (Table 2) and (iii) weaker fits of trend lines based on aerobic counts were observed for results plotted against UV light as those for total sunlight (Figure 3), with no evidence of any stronger relationships based on UV data than those for total sunlight. This demonstrates that total sunlight is as good a predictor of solar photocatalysis in these TFFBR experiments as UV light.

Figure 4
figure 4

Effect of different flow rates (a) 4.8 L h-1, (b) 8.4 L h-1 and (c) 16.8 L h-1, on log inactivation of A.hydrophila ATCC 35654 in spring water run through the TFFBR under different Ultraviolet (UV) light conditions. Enumeration was aimed at under standard aerobic condition (open circle) and under ROS-neutralised condition (closed circle).

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Table 2 Linear regression equations and R2 values of A.hydrophila ATCC 35654 inactivation against UV light intensities under 3 different flow rates
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Discussion

While earlier studies have mostly concentrated on the application of TFFBR systems for chemical degradation, TiO2-based photocatalysis has proved its ability to enhance the rate of inactivation of microbes in contaminated drinking waters and waste waters, enabling such waters to be disinfected [20, 21]. The present study has clearly shown that A. hydrophila ATCC 35654 can be effectively inactivated in spring water using the TFFBR under sunlight conditions of > 600 W m-2, demonstrating its potential for applications in aquaculture, especially in tropical and sub-tropical developing countries where sunlight is abundant and the resources for alternative forms of disinfection are scarce.

The efficiency of the TFFBR was also investigated in this study by flowing (at 4.8 L h-1) contaminated spring water sample under high sunlight intensities and by using same sized glass with and without TiO2 under the same reactor conditions. The findings of this study confirm the results of two previous studies [7, 21]. The presence of TiO2 showed a clear enhancement in solar photocatalysis [21]. The current study clearly shows that solar energy alone is unsufficient to inactivate A. hydrophila and that a photocatalyst such as, TiO2 is required for effective reduction in counts.

Microbial disinfection by solar photocatalysis is a complex and challenging process [30]. The extent of inactivation observed in A. hydrophila ATCC 35654 under high sunlight intensity was also found to be similar to that reported for other microbes in early studies [8, 16]. Thus one investigation showed that when the UV irradiance was 20-43 W m-2, the inactivation of the fungus Fusarium sp. was faster than than at lower irradiances (cloudy weather condition), using a CPC reactor [8]. Similar effects of solar irradiation on inactivation were observed in the present study, under different sunlight condition. For example, at lower sunlight conditions (total sunlight intensity = 300-600 W m-2 or UV irradiance = 20-40 W m-2) inactivation was considerably less than was observed at the highest sunlight conditions (> 1100 W m-2 and > 65 W m-2) at 4.8 L h-1. Solar photocatalytic activity was also demonstrated for various pathogens in drinking water in a batch culture reactor using simulated sunlight [16], in contrast to the TFFBR system tested under natural sunlight used in the present study. Similarly, recent studies have succeeded in photocatalysis but they required a long UV exposure times to achieve a log inactivation of 6-fold for E.coli K12 using a CPC pilot plant solar reactor [7, 21]. Such inactivation is far greater than that observed in the present study, where the log inactivation was around 1.38 with an average initial count of 1.36 × 105 CFU mL-1 and average final count of 5.10 × 103 CFU mL-1, at the highest sunlight intensities--this is most likely due to the rapid transfer of contaminated liquid across the TFFBR plate, which is around 2.5 min at 4.8 L h-1flow rate, in the present study. As most previous studies have used an artificial UV light source for exposure, it is difficult to make direct comparisons to the present study, where natural sunlight has been used. Additionally, different type of reactors will have different dynamics of inactivation and flow, as well as dissimilar kinetics of change with light intensity.

Counts of A. hydrophila ATCC 35654 exposed to the TFFBR system at low sunlight (< 600 W m-2) under ROS-neutralised conditions were substantially higher than those obtained from standard aerobic plate counts, which validates the finding from previous studies of E. coli and other bacteria [22–24]. This indicates that the antioxidant system of many cells of A. hydrophila ATCC 35654 was damaged by solar photocatalysis at low sunlight intensities, resulting in their sensitivity towards their own respiratory by-products. Such cells were only able to form colonies when sodium pyruvate (a scavenger of hydrogen peroxide) is added, coupled with growth under anaerobic conditions, which will enable the bacteria to use fermentative pathways, rather than aerobic respiration, for energy generation. The findings of this present study unequivocally demonstrate that at all three different flow rates tested, at low sunlight intensities (< 600 W m-2) there was a substantial difference between the log inactivation results based on ROS-neutralised and conventional aerobic counts (Figures 3 and 4). At 4.8 L h-1, there was close to 1 log difference between the ROS-neutralised and aerobic log inactivation results, suggesting that the aerobic data provide an apparent inactivation that overestimates the true value. For other two flow rates (8.4 and 16.8 L h-1) the difference between the two sets of data were around 0.9 and 0.5 (with similar initial inoculam of 1.33 × 105 CFU mL -1 and final count of 9.40 × 103 and 1.75 × 104 CFU mL-1) respectively, indicating a reduction in the amount of sub-lethal injury at higher flow rates that is also coupled with a lower overall inactivation (Table 1). While previous studies of solar disinfection have demonstrated sub-lethal injury and ROS-sensitivity in batch culture with uncalatysed reactors, this is the first study to do so for the TFFBR continuous flow photocatalytic system. On the other hand, at higher sunlight intensities (> 600 W m-2), the differences between the results based on aerobic counts and ROS-neutralised counts were negligible for all flow rate conditions, demonstrating the strength of high sunlight to provide powerful inactivation, with no sign of sub-lethal injury.

Sometimes, sunlight itself is not sufficient for water disinfection, due to the effectiveness of photoreactivation mechanisms in microorganisms [31]. A recent study has demonstrated the effectiveness of immobilised TiO2 reactors in inactivating bacteria to such an extent that their photoreactivation mechanisms are not able to repair the damage [19], indicating that fixed-bed TiO2 reactors increase the extent of damage to bacteria from the very beginning of the process, whereas TiO2 slurry systems required longer irradiation times to cause an equivalent amount of cellular damage. In a slurry system, TiO2-related damage occurs at the cell membrane of bacteria; however, damage is distributed across the whole membrane, so membrane permeability effects are not always strong enough to cause irreversible inactivation in the early stages of the process. On the other hand, in a fixed-bed reactor, while the free radicals generated may be lower in number, the damage can be concentrated on the cell membrane area, causing inactivation [19]. The result of the current study can be interpreted in similar approach, but with respect to sunlight intensity. Here it was observed that while low sunlight resulted in substantial sub-lethal injury, with results based on ROS-neutralised counts being far lower than for aerobic data, at higher light intensities, ROS neutralised data were similar to those based on aerobic counts. As the data at high sunlight intensities showed little evidence of sub-lethal injury, this demonstrates that the TFFBR system will be more efficient in full sunlight, where maximum inactivation is achieved.

The dynamics of flow rate in pilot-scale photocatalytic reactors have not been well studied to date. In considering treating large volumes of water, as in aquaculture systems, it is obvious that flow rate will be a crucial parameter. A pilot-scale CPC reactor using TiO2 in suspension with different flow rates has been used to study the inactivation of Fusurium sp. spores [18]; achieving the highest inactivation rate of Fusurium spores at a flow rate of 30.0 L min-1 with added TiO2 at 100 mg L-1 concentration. However, such systems require separation of the suspended TiO2 after treatment, which adds to the complexity, in contrast to immobilised systems such as the TFFBR. Another recent solar disinfection study also showed the importance of evaluating different parameters including: flow rate; water volume within the reactor; temperature; and solar energy [32]. They used a CPC reactor with no added TiO2 and suggested that increasing flow rate has a substantial negative effect on the inactivation of bacteria, which is in agreement with the flow rate investigations of the present study. Here, the lowest flow rate of 4.8 L h-1 was found to be the most effective for inactivation of A. hydrophila ATCC 35654 as the residence time of 2.5 minin the 4.8 L h-1 experiment is almost twice as high as the 8.4 L h-2 experiment.(86 s) Similarly, when the total sunlight intensity is at average of 1000 W m-2, the cumulative energy, 150 KJ m-2 at 4.8 L h-1 is higher than that of 86 KJ m-2 at 8.4 L h-1 which will play a major role A. hydrophila inactivation. In this study, the water temperature in the reservoir was maintained at (22-23)°C throughout the experiments. Due to the open structure of the TFFBR, the temperature of the water on the reactor plate was not measured, though it is logical to expect that it would be positively related to sunlight intensity.

Conclusion

The results clearly demonstrate that high sunlight intensities (> 600 W m-2) and low flow rates (4.8 L h-1) provide optimum conditions for the inactivation of the fish pathogen A. hydrophila ATCC 35653, with fewer injured (ROS-sensitive) cells under such conditions than at lower sunlight intensities. Using a TFFBR system to disinfect these bacteria under natural sunlight is a novel and alternative approach to conventional chemical disinfectants and antibiotics for control of this pathogen. The present study is also the first to report sub-lethal injury for a solar photocatalytic system at low sunlight intensities (< 600 W m-2), which places a question mark over conventional aerobic counts under such conditions and demonstrates that ROS-neutralised conditions are required to enumerate survivors of solar photocatalysis at low sunlight levels. However, conventional aerobic counts should be effective in enumerating A. hydrophila ATCC 35653 surviving a TFFBR system operating under high sunlight conditions, making it easier to assess efficiency under such conditions. Overall, the use of solar photocatalysis represents a potential low-cost, sustainable approach across all countries with consistent sunny climates.