1. Introduction
Anthracnose (caused primarily by
Colletotrichum spp.) and stem end rot (caused by
Colletotrichum spp., Botryosphaeriaceae fungi and others) are considered the most serious postharvest diseases of avocado fruit that result in considerable losses during storage and marketing [
1,
2]. Generally, synthetic fungicides such as Sportak (450 g L
−1 prochloraz) and Graduate A+ (200 g L
−1 azoxystrobin and 200 g L
−1 fludioxonil), are used in packing lines to reduce losses caused by postharvest diseases, and follow a field fungicide program [
3,
4]. Markets are becoming increasingly sensitive to pesticides applied to food through growing cycles and after harvesting, and maximum residue limits (MRLs) are becoming stricter, with alternative pest and disease reduction measures being sought.
In addition to the application of synthetic fungicides, different types of chlorine-based sanitizers are used in harvested fruit and vegetables to reduce microbial load prior to packaging. Liquid chlorine, hypochlorite, inorganic and organic chloramines, chlorine dioxide, and hypochlorous acid are common chlorine-based sanitizers. In practice, chlorine-based sanitizers are produced as highly concentrated and corrosive chemical solutions, which are diluted before use, and therefore introduce workers’ health and safety issues during storage and application [
5,
6].
Electrolyzed oxidizing (EO) water (also known as electro-activated water or ionized water solution) has been reported to be highly microbiocidal against bacteria, viruses, fungi, and protozoa and may represent an alternative to synthetic chemicals and traditional chlorine-based sanitizers [
5,
7,
8,
9]. EO water is generated by electrolysis of a dilute salt (NaCl) solution in an electrolysis chamber where anode and cathode are separated by a membrane or diaphragm and two types of electrolyzed water are generated simultaneously. At the anode, acidic electrolyzed water with a pH of 2–3 and oxidation-reduction potential (ORP) >1100 mV is produced, whereas at the cathode, basic electrolyzed water with a pH of 10–13 and ORP of 800 to 900 mV is produced. Neutral electrolyzed water with a pH of 7–8 and ORP of 750–900 mV is produced by mixing the anodic solution with OH
− ions or by using a single-cell unit without diaphragm [
6,
10,
11].
EO water exerts its antimicrobial effects due to its high ORP and concentration of available chlorine species such as hypochlorous acid and hypochlorite ions [
12,
13], and their respective levels determine the efficacy of EO water and other chlorine-based solutions as sanitizers [
14,
15,
16]. It is now common for postharvest processors to monitor ORP (in mV) as well as chlorine dose (in ppm) as both parameters contribute to antimicrobial potential [
17]. An oxidizing solution with high ORP takes electrons away from microbial cell membranes, causing collapse of the cell [
17]. Solutions with higher ORP possess greater oxidizing strength compared to solutions with weak ORP [
16]. EO water with high ORP, that is, 800–1000 mV may be considered as an effective sanitizer against microorganisms. Active chlorine content (ACC) refers to the amounts of active chlorine such as chlorine gas (Cl
2), hypochlorous acid (HOCl), and hypochlorite ions (OCl
−) present in solution. Both HOCl and ClO
− inactivate pathogenic and spoilage bacteria through oxidative damage to cell membranes [
18]. pH determines the available forms and concentrations of ACC in EO water solution, and OCl
−, HOCl, and Cl
2 are the predominant forms at high, neutral, and low pH, respectively [
7,
9,
19]. Commercial bleach such as calcium or sodium hypochlorites have OCl
− ions, whereas the major active antimicrobial and sporicidal agent in neutral EO water is HOCl, which is the stronger oxidant due to its higher ORP and is 80 times more antimicrobial compared with OCl
− [
20]. Hypochlorous acid as the dominant species in water is more desirable than hypochlorite ions for effective disinfection and oxidation due to its higher standard electrode potential, or electromotive force, driving the reduction half-reaction [
19].
EO water in neutralized form has low corrosion potential and is reasonably stable in pure form. EO water can evaporate or become deactivated when it reacts with organic matter, and can be diluted with tap water, or removed by reverse osmosis [
21]. EO water has low chemical impacts on the environment because it uses only low levels of salt solution with no other added chemical compounds [
12]. Furthermore, as it can be produced on-site, there is a reduced risk of chemical exposure to skin during transport, storage, and handling as compared to the concentrated bleach compounds [
22].
A previous study evaluated anthracnose and stem end rot of avocado after dip treatment in chlorine-based or quaternary ammonia sanitisers [
23]. A three-fold commercial concentration (900 ppm) of the chlorine test solution reduced anthracnose compared with water dip control; however, stem end rot was increased [
23]. Although there are no reports relating to the effectiveness of EO water to reduce postharvest diseases in avocado, there are a few studies demonstrating that field applications or postharvest treatment reduced development of disease and improved shelf life in some plants and harvested fresh produce. For example, EO water was found to be effective in the management of infection of
Botrytis cinerea on strawberry plants in the field where application of 100 ppm EO water twice per week was more effective than a once per week fungicide (Captan) application [
24]. Fujiwara et al. [
25] reported that the severity of powdery mildew infection on cucumber leaves was reduced by successive sprays of EO and electrolyzed reducing water.
EO water disinfestation is already in use in a diverse array of food processing plants in Australia [
26]. It has been easily implemented into existing packing line infrastructure and has a low on-going cost after initial installation of generating equipment [
8,
10,
21,
27,
28]. Because there are few reports on the reduction of postharvest diseases of fruit using EO water, the present study was undertaken to examine the efficacy of treating avocado fruit with EO water on the severity of postharvest diseases and shelf life, compared with industry standard fungicides and a common chlorine-based sanitizer.
2. Materials and Methods
2.1. Trials Conducted
Table 1 summarizes the treatments and replication included in each of the five trials, which were conducted between April and September 2018. Mature hard avocado fruit of uniform size and shape and free from visible disease symptoms were sourced from a non-sprayed orchard in northern New South Wales (trials with cv. Hass) or from an orchard near Bundaberg of Queensland, which received copper sprays throughout the season but had not received pre-harvest azoxystrobin fungicide spray (trial with cv. Wurtz). Fruits were transported to the laboratory facilities at Ecosciences Precinct, Dutton Park, Queensland (Trials 1–4) or Maroochy Research Station, Nambour, Queensland (Trial 5). Dry matter contents of the experimental avocados for all the trials were determined by drying cores of flesh at 45 °C for 2–3 days, and were between 24% and 34%. All batches of fruit had exceeded the minimum commercial maturity standard set by the Australian industry (23% for Hass).
Experimental fruit were dipped in treatment solutions in their replicate batches for 30 s except for Trial 5 (
Table 1), dried at ambient temperature, and re-packed into avocado trays. Trial 1 examined the effects of various concentrations of electrolyzed oxidizing (EO) water and industry standard fungicides (Sportak and Graduate A+) on postharvest diseases of avocado resulting from natural field infection. Trial 2 was similar to Trial 1 but only anthracnose disease arising from inoculation with
Colletotrichum siamense was assessed. Trials 3 and 4 were repeat experiments with cultivars Wurtz and Hass that examined the effects of EO water, fungicide, and commercial bleach (sodium hypochlorite) on postharvest diseases arising from both natural infections and inoculation. Trial 5 was undertaken to confirm the results of previous trials and evaluated EO water and Graduate A+ fungicide in an experimental-scale sprayline. The treated fruit from all the trials were maintained in a controlled environment ripening room at 22–23 °C and 65–70% relative humidity to optimize expression of postharvest diseases. All the trials were laid out in completely randomized designs (CRD).
2.2. Application of Postharvest Treatments
Electrolyzed oxidizing (EO) water was provided for testing by Mr. Mark Parkinson, Lockyer Agronomics, Gatton, Queensland, facilitated by Mr. Keith Mason, Envirolyte Australia. EO water solutions of desired concentrations were prepared by mixing EO water of 100% v/v with tap water. Concentrations of EO water for testing were determined on the basis of previous reports. Different concentrations were tested in Trials 1 and 2, and in subsequent trials 20% v/v was selected as 10%, 20%, and 30% v/v EO water produced statistically similar results.
Graduate A+ (active ingredients 200 g L−1 azoxystrobin and 200 g L−1 fludioxonil) was sourced from Syngenta Crop Protection Pty Ltd., 2–4 Lyon Park Road, NSW 2112, Australia. The registered label rate of Graduate A+ was prepared by mixing Graduate A+ at 2.5 mL L−1. Sportak (450 g L−1 prochloraz as active constituent) obtained from FMC Australasia Pty Ltd., was prepared at the label rate of 0.55 mL L−1.
Sodium hypochlorite (NaOCl), 100 mg L−1, was prepared from commercial bleach of 125 g L−1 active constituent as sodium hypochlorite (HY-CLOR Australia Pty Limited, New South Wales). A total of 8 mL of concentrated bleach was added to 10 L of water in a plastic bucket.
For Trials 1–4, adequate quantities of each treatment solution (5–10 L) were prepared in plastic buckets, and fruit were dipped for 30 s then allowed to air-dry on racks. Fruit were then repacked in the avocado trays and maintained in the controlled environment room as described previously. However, for Trial 5, fruit were rotated on rollers while pre-washed with tap water from overhead spray (to waste) for approximately 10–15 s. Fruit were then advanced to rotation by brushes, and treatment solutions were applied by recirculating overhead spray from a 200 L tank for 30 or 60 s. The treated fruit were allowed to air dry, packed in avocado trays, and were transported to Ecosciences Precinct, Dutton Park, Brisbane, and held in a controlled environment room for observation.
2.3. Measurement of pH, Oxidation Reduction Potential (ORP), and Free Chlorine in Treatment Solutions
Oxidation reduction potential (ORP), pH, and free chlorine (hypochlorite, ClO−) of the prepared EO water solutions in Trials 2–5 were measured. Samples of approximately 100 mL were taken in triplicate from the test solutions. pH and ORP were measured immediately after preparation of the solutions, and free chlorine was measured within 72 h of preparation.
The oxidation reduction potential of the EO water solutions and the control (tap water) were determined using an ORP meter (Milwaukee 500 ORP Meter). The electrode of the ORP meter was inserted into the solutions and measurements were taken when the reading stabilized. pH was measured in 20 mL samples using a standard laboratory pH meter (Met Rohm, PC).
Free chlorine is the sum of hypochlorous acid (HOCl) and hypochlorite ion (ClO
−). In the present study the concentration of ClO
− in the treatment solutions was determined by redox titration as per the method described by Dr. Richard Walding, Griffith University, Australia (downloaded from:
http://seniorchem.com/chlorine_thiosulfate_titration.pdf). This method involves converting the hypochlorite ion (ClO
−) of bleach solution to iodine (I
2) by the addition of KI and then titrating resultant iodine with thiosulfate (S
2O
32−) solution, which can be visualized by the change from brown to slight yellow color. As this end-point is difficult to detect, starch indicator is added, forming a blue complex with iodine. As the iodine reacts with thiosulfate, the blue color disappears, indicating the reaction end-point. The titre value was then used for calculation of concentration of the free chlorine (as ClO
−) in the treatment solutions, given that 1 mole of ClO
− is equivalent to 2 moles of S
2O
32−. The concentration of hypochlorite ions was then calculated using the formula: C (hypochlorite) × V (hypochlorite) = C (thiosulfate) × V (thiosulfate)/2. The concentration is expressed in ppm (mg L
−1) using the formula, C (ClO
−) = C (ClO
−) × M (ClO
−), where M (ClO
−) is the molecular mass of hypochlorite (51.5 g mol
−1).
2.4. Fruit Inoculation
Apart from the assessment of postharvest diseases arising from natural field infections (Trials 1, 3, 4, and 5), fruit were also inoculated (Trials 2, 3, and 4) to determine efficacy of treatments when applied prior to pathogen infection. One day after dipping in chlorine-based or fungicide solutions, fruit were removed from the trays and placed on racks within plastic boxes (20 × 12 × 6 cm), which had been lined with moistened paper towels to create a humid environment. Circles approximately 1.0–1.5 cm diameter were drawn on two positions on each fruit to indicate sites for inoculation. A 20 µL droplet of conidial suspension (10
6 conidia mL
−1) of
Colletotrichum siamense (originally isolated from avocado, BRIP 63702) was placed within the circles (
Figure 1A). The boxes were sealed to maintain high humidity for 24 h to facilitate spore germination and infection of fruit. After the incubation period, fruit were removed and placed back into their avocado trays within the ripening room.
2.5. Fruit Assessment
Softness (mm deformation) of fruit was assessed at eating ripe stage using non-destructive fruit firmness tester [
29]. A 500 g weight was applied to each of the fruit and the deformation was recorded in mm after 30 s.
Fruit were checked daily for ripening and when deemed “eating ripe” (as determined by hand pressure test and color) each piece was removed from the ripening room and assessed for severity of postharvest disease arising from natural field infection. Hass fruit peel becomes dark purple/black upon ripening, thus peeling is necessary in order to see and quantify the progression of postharvest disease. The percentage of fruit surface area affected by side rots (mostly anthracnose) was determined by visual assessment. Stem end rot (percent fruit volume affected) was determined by visual estimation after slicing fruit transversely and rating for internal disease severity arising from the stem. Incidence (percent numbers of fruit affected) of anthracnose and stem end rot was also determined. Fruit that were inoculated were peeled, and the diameters of lesions at the inoculation point were measured (two perpendicular measurements per lesion). The lesion was assumed circular and the area was calculated by using the formula πr2. The number of days from harvest to eating ripe was determined for each treatment. Incidence and severity of anthracnose and stem end rot for the variety Wurtz were determined on the basis of external symptoms without peeling as the fruit remain green when ripe.
2.6. Data Analysis
Data were analyzed using IBM SPSS Statistics (Version 25). For percentage data, arcsine transformations were carried out to satisfy assumption of ANOVA and analysis was performed on the transformed data. Mean separations were performed according to least significant difference (LSD) test post hoc only where significant treatment effects were found.
4. Discussion
There was a consistent effect of electrolyzed oxidizing (EO) water and postharvest fungicide (Graduate A+) in reducing postharvest diseases of avocado, particularly stem end rot, arising from natural field infections. In the case of natural infection, 5%, 10%, or 20% (v/v) EO water significantly reduced the severity of stem end rot disease compared to water-treated control fruit in all four trials where it was assessed. Control of SER was statistically similar to that achieved by Graduate A+, a fungicide registered in Australia for postharvest application for avocado since 2018 that is known to be particularly effective against stem end rot.
Fruit were sourced from orchards that had not been sprayed with copper fungicides throughout fruit development; consequently, anthracnose disease arising from natural field infections was extremely high in all four trials where it was assessed, with incidence (numbers of fruit) frequently at 80–90% with corresponding high severity (percent of surface area affected) at more than 50%. Under such high disease pressure, EO water, bleach, as well as the fungicide treatments were ineffective, except in Trial 1 where both tested fungicides reduced severity, and Trial 5 where both 20% EO water and fungicide Graduate A+ applied under simulated commercial conditions reduced disease compared with water controls. A combination solution of EO water and fungicide was not included in the present study, but obviously further work should include this combination to assess whether there are additive effects, resulting in even greater reduction of postharvest disease in avocado.
A commercial bleach solution, sodium hypochlorite (NaOCl), was assessed alongside 20% v/v EO water and fungicide Graduate A+ in two fruit dipping trials. There were no effects of any treatment on anthracnose, as discussed above. In one trial, reduction in stem end rot after NaOCl was not significantly different from water controls, and in the other trial, it reduced SER significantly compared with water but was still twice as severe as that in 20% v/v EO water and Graduate A+-treated fruit.
Anthracnose and stem end rot were significantly reduced due to application of EO water and Graduate A+ fungicide via an experimental packing line, simulating commercial practice. Overhead spray treatment while fruit were rotated on brushes for 30 or 60 s in EO water solution or Graduate A+ had statistically similar impacts on reduction of postharvest diseases.
Although this is the first report demonstrating efficacy of EO water to reduce postharvest diseases in avocado, there are a few reports on other fresh produce that support the findings of the present research. Effects of surface disinfectants (chlorinated water at 100 mg kg
−1, EO water of pH 6–7, hot water at 53 °C for 20 s, and biocontrol agent, namely, B13 yeast, a strain of
Candida fermentati) were evaluated for effects on postharvest quality of kumquat citrus (
Fortunella sp.) [
30]. Fruit treated with a combination of EO water, hot water, and biocontrol agent displayed no visible growth of mold fungi during the 28 day storage period. However, chlorinated water (100 mg kg
−1; pH of 7.0–7.2) alone produced the highest decay (13.6%), whereas fruit subjected to EO water only displayed significantly reduced level of decay (4.08%) as compared to chlorinated water by 28 days, suggesting potential of enhanced efficacy from combined applications of the control agents. The study concluded that integration of EO water, hot water, and biocontrol was among the most effective treatments in maintaining quality of kumquat fruit. In another study, EO water was also tested on date (
Phoenix dactylifera) to improve shelf life and quality by reducing microbial population [
31,
32]. Dates were dipped in EO water solutions (pH 7–7.5; ORP 800–850 mV) at three concentrations (1%, 3%, and 5%) and for various durations (0 to 4 min). Total counts of mesophilic bacteria was reduced by up to 99.5% and yeast and molds were completely eliminated.
In the present study, lesions arising from inoculation of harvested avocado fruit with the anthracnose pathogen,
Colletotrichum siamense, were significantly smaller in two of the three trials where assessed, with indications of reduction in the third trial. This indicates a protective effect of EO water application, and suggests that sprays in the field during fruit development may contribute to lower disease and improved quality through the supply chain. A study conducted by Guentzel, Callan, Liang Lam, Emmons, and Dunham [
24] reported that EO water of near neutral pH (6.3–6.5) was found to be effective to manage infection of
Botrytis cinerea on strawberry plants in the field and also as a disinfection solution for harvesting equipment, greenhouses, packing houses, and in commercial facilities to prevent or limit infections of
B. cinerea and
Monilinia fructicola. Application of 100 ppm EO water twice per week to strawberry plants infected with
B. cinerea was more effective than a once per week fungicide (Captan) application [
24]. Fujiwara, Fujii, and Park [
25] reported that the severity of powdery mildew infection and phytotoxic symptoms on cucumber leaves sprayed successively with EO and electrolyzed reducing water were reduced compared with EO sprays only. An in vitro assessment showed that germination of 22 test fungi was significantly reduced or prevented by EO water [
33]. All relatively thin-walled species (e.g.,
Botrytis sp.,
Monilinia sp.) were killed by incubation times of 30 s or less. Thicker-walled, pigmented fungi (e.g.,
Curvularia sp.,
Helminthosporium sp.) required 2 min or longer for germination to be reduced significantly [
33]. There is likely to be a direct inhibitory effect of EO water on avocado fungal pathogens, and this will be confirmed in future work.
Firmness and shelf life are important postharvest quality parameters for fresh fruit and vegetables, and may determine market destination. In the present study, postharvest treatments mostly had no significant effects on number of days to ripen and firmness, measured by instrumentation. In two trials, Graduate A+ fungicide-treated fruit was significantly less firm than fruit in all other treatments, with the exception of Sportak in the first trial. Treated fruit took significantly longer (approximately 1–2.5 days) to ripen than water-treated fruit in one trial where fruit was inoculated with
C. siamense. A similar finding was also reported by Workneh et al. [
34], who demonstrated that disinfecting treatments (EO water and chlorinated water) had no significant effects on firmness, total soluble solid content, and the overall visual appearance of carrots. Sensory assessment showed no significant difference related to taste, odor, texture, and color of treated dates [
32]. Recent biochemical studies in blueberries reported that EO water treatment delayed softening of blueberries, most likely through deactivation of cell wall-degrading enzymes [
35] and regulation of reactive oxygen species [
36], maintaining cellular integrity for a longer period compared with untreated fruit. Although there were no visible effects of EO water on harvested avocado fruit in the current study, future field or postharvest applications to foliage, fruit, or roots should be carefully monitored for any phytotoxic damage that could reduce yields or negatively impact quality.
Apart from ORP, the antimicrobial properties of available chlorine species hypochlorous acid (HOCl) and hypochlorite ions (OCl
−) in EO water may also contribute to the reduction of postharvest diseases of avocado in the current study. Free chlorine is the sum of hypochlorous acid and hypochlorite (HOCl + OCl
−) that plays a vital role in the disinfection processes [
15]. Chlorine causes direct damage to cell membrane of microorganisms, making them permeable, resulting in cell inactivation due to damage of the key organelles by the chlorine [
15]. Gray [
15] reported that for chlorination to be effective against bacteria and viruses, water should have a pH <8.0 with a chlorine dose sufficient to produce a free chlorine residual of 0.5 mg L
−1 over a contact time of 30 min. For inactivation of
E. coli free chlorine concentration of 0.03 mg L
−1 per min is required at 25 °C [
15]. For
E coli O157H7,
Salmonella typhi, and
Shigella sonnei, the free chlorine concentrations required per min for inactivation were 0.1 mg L
−1 at 21 °C, 0.5 mg L
−1 at 25 °C, and 0.5 mg L
−1 at 25 °C [
15], respectively. These findings were in support of the results of the present investigation where the free chlorine (hypochlorite ions) levels of the EO water solutions ranged from 0.1 to 0.2 mg L
−1.
The concentration of HOCl was not determined directly in the current study, however, both HOCl and OCl
− have disinfection properties. The degree of dissociation of HOCl is pH-dependent and gradually decreases as the pH falls; for example, at pH <5.0, approximately 100% of the chlorine is in HOCl form, which falls to 50% at pH 7.5, whereas at pH >9.0, 100% of chlorine is present as OCl
−. EO water generally exerts its maximum effects at neutral pH [
7,
9,
32] and with ORP of more than 850 mV [
16]. In the present study, the pH of 20%
v/
v EO water solutions were 7.2 to 8.2, and ORP 795–906 mV, compared with hypochlorite bleach solutions (two trials) which had higher pH of 8.8–9.4 and lower ORP of 734–767 mV. Neutral pH and the possible higher activity of HOCl in the case of Trial 5 (experimental packing line) may have contributed to the significantly reduced severity of both natural anthracnose and stem end rot diseases. By contrast, higher pH and lower ORP of the sodium hypochlorite solutions resulted in higher levels of infections that were statistically identical to control fruit despite having similar or higher concentration of OCl
− species.
Although not determined in the current study, it is likely that EO water would reduce foodborne (human) bacterial pathogens such as
Salmonella spp.,
Listeria monocytogenes, and
Escherichia coli on avocado fruit surfaces and in processed pulp products. A recent survey by the United States Food and Drug Administration reported a high incidence (18%) of
Listeria sp. detected on avocado skin samples, with equal numbers from domestic versus imported sources testing positive [
37]. There was a lower incidence (3.3%) of
Salmonella spp. detected. Similar low levels (2.3%) of
Listeria was present in processed avocado or guacamole product, where most of the tested samples were of U.S. origin. Another study in South Africa reported a high incidence (14%) of
E. coli, 2.4% of
Salmonella sp., and no
Listeria sp. from skin and pulp samples [
38].
EO water has been approved by regulatory authorities for use as a sanitizer in the food industry. It has been approved for the use in organic production by the United States Department of Agriculture (USDA) in 2015 through a USDA memorandum [
39] updating the status of electrolyzed water under USDA Organic Regulations. In the United States, it is also approved by the Food and Drug Administration (FDA) for cleaning and sanitizing purposes [
9,
32]. EO water is also used in hospitals, food facilities, and agricultural venues in the European Union as disinfectant [
31,
32]. In Australia, e-Waters Systems has recently (August 2018) received HACCP certification (the international standard defining the requirements for effective control of food safety), for their two models of generators of food-safe cleaning and sanitizing liquids, known as EO water, suitable for use in food facilities and food handling operations [
40].