Front. Plant Sci. Frontiers in Plant Science Front. Plant Sci. 1664-462X Frontiers Media S.A. 10.3389/fpls.2021.775629 Plant Science Review Fresh Produce Safety and Quality: Chlorine Dioxide’s Role Malka Siva Kumar Park Me-Hea * Postharvest Research Division, National Institute of Horticultural and Herbal Science, Wanju-gun, South Korea

Edited by: María Serrano, Miguel Hernández University of Elche, Spain

Reviewed by: Mark Morgan, The University of Tennessee, Knoxville, United States; Charu Gupta, Amity University, India; Maria Concetta Strano, Council for Agricultural and Economics Research (CREA), Italy

 *Correspondence: Me-Hea Park, poemmich@korea.kr

This article was submitted to Crop and Product Physiology, a section of the journal Frontiers in Plant Science

 11 01 2022 2021 12 775629 14 09 2021 16 12 2021 Copyright © 2022 Malka and Park. 2022 Malka and Park

This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

Maintaining microbial safety and quality of fresh fruits and vegetables are a global concern. Harmful microbes can contaminate fresh produce at any stage from farm to fork. Microbial contamination can affect the quality and shelf-life of fresh produce, and the consumption of contaminated food can cause foodborne illnesses. Additionally, there has been an increased emphasis on the freshness and appearance of fresh produce by modern consumers. Hence, disinfection methods that not only reduce microbial load but also preserve the quality of fresh produce are required. Chlorine dioxide (ClO2) has emerged as a better alternative to chlorine-based disinfectants. In this review, we discuss the efficacy of gaseous and aqueous ClO2 in inhibiting microbial growth immediately after treatment (short-term effect) versus regulating microbial growth during storage of fresh produce (long-term effect). We further elaborate upon the effects of ClO2 application on retaining or enhancing the quality of fresh produce and discuss the current understanding of the mode of action of ClO2 against microbes affecting fresh produce.

 chlorine dioxide fresh produce microbial safety log reduction produce quality storage shelf life antimicrobial mechanism Rural Development Administration10.13039/501100003627 Introduction

Fresh produce, including fruits and vegetables, is a good source of nutrients and an important component of a healthy and balanced diet. However, fresh produce is susceptible to microbial contamination, which may occur at any step of the food supply chain, from sowing the crop to delivering it to the customer. Furthermore, cross-contamination can occur during processing, packaging, or transporting fresh produce. Most common sources of food contamination are soil, animal manure, and irrigation water, and consuming contaminated food may lead to the outbreak of foodborne illnesses. In the United States of America, 340 foodborne outbreaks, from 2009 to 2018, were associated with fresh produce (CDC, 2018). Furthermore, 5,175 foodborne outbreaks were reported in Europe in 2019, involving 49,463 cases, 3,859 hospitalizations, and 60 fatalities (European Food Safety Authority, 2021). Foodborne diseases not only affect human health but also pose challenges to tourism, agricultural, and food industries, thereby seriously affecting socioeconomic development (WHO, 2015).

Microbial contamination can affect the quality and shelf-life of fresh produce. In 2010, an estimated 31% of the total food produce worth $161.6 billion was declared unfit for human consumption at the retail and consumer levels (Buzby et al., 2014). With an increased awareness of the importance of fresh produce consumption for a healthy lifestyle, the concerns of modern consumers regarding the freshness, appearance, and microbial safety of fresh produce have increased. At the retail level, primarily in supermarkets and hypermarkets, 15–30% of the fresh produce was rejected by consumers because of quality standards that over-emphasize appearance (FAO, 2011). Hence, microbial safety and high quality have emerged as a concern for the food industry and consumers.

Several physical and chemical disinfection methods have been used to reduce the microbial load on fresh produce (Deng et al., 2020; Chacha et al., 2021). However, a potent disinfection method must fulfill the following criteria: high efficacy against pathogens, ability to reduce microbial spoilage, potential to retain nutritional quality, no formation of intolerable levels of human toxic by-products or residues, and no environmental impact (Joshi et al., 2013). The efficacies of various physical disinfection methods, including high hydrostatic pressure, cold plasma, ultraviolet, ultrasound, pulsed, and ionizing radiation, have been examined. However, these methods have various disadvantages. For instance, ultrasound shows limited antimicrobial effect, ultraviolet light has low penetration and shade effect from complex surface properties of produce affects its efficiency, and pulsed light increases temperature that deteriorates the quality of treated produce (Deng et al., 2020).

Chlorine is the most commonly used chemical disinfectant in the food industry, which is effective against a broad range of pathogens and whose efficacy has been evaluated in a wide variety of fresh produce (Praeger et al., 2018). However, chlorine may react with natural organic matter and form halogenated by-products, such as trihalomethanes or haloacetic acids (Praeger et al., 2018). These by-products are carcinogenic and not environment-friendly. Moreover, owing to safety and efficacy concerns, the use of chlorine for the sterilization of fresh-cut produce has been banned in countries such as Belgium, Switzerland, and Netherlands (Deng et al., 2020). Therefore, several chemical alternatives, such as chlorine dioxide (ClO2), ozone, electrolyzed water, essential oils, high-pressure carbon dioxide, and organic acids, have been identified or proposed (Deng et al., 2020). For instance, electrolyzed water, and ozone are potent disinfectants; however, for the effective microbial reduction high concentration or prolonged exposure is required. Excessive usage of these treatments can negatively affect produce quality (Deng et al., 2020). Organic acids are safe and easy to use but their antimicrobial efficiency is limited. Essential oils are natural antimicrobial agents; however, it is practically difficult use these oils because of their hydrophobic, volatile and unstable nature (Deng et al., 2020).

Application of ClO2, an oxidative gas, is effective in controlling the bacterial, fungal, and viral contamination of fresh produce (Praeger et al., 2018; Sun et al., 2019). In contrast to chlorine, ClO2 neither produces toxic by-products nor does it alter the nutritive and organoleptic qualities of food products, and is effective over a wide pH range (pH 3–8). In addition, it is widely used as a bleaching agent in paper industry and as a disinfectant in laboratories, hospitals, public places, and other areas (Praeger et al., 2018). Owing to its efficacy and safety, ClO2 has been approved for the disinfection of fresh produce and in food processing industries (FDA, 2008). Recently, Praeger et al. (2018) and Sun et al. (2019) comprehensively reviewed antimicrobial activity of aqueous and gaseous ClO2, respectively. This review focuses on the effects of ClO2 application on the initial reduction in microbial growth (short-term effect) and the final reduction in microbial populations during the storage of fresh produce (long-term effect). We further discuss the efficacy of ClO2 application in maintaining the quality of fresh produce and the action mechanism of ClO2 against microbes affecting fresh produce.

 Modes of Chlorine Dioxide Application

Chlorine dioxide is a yellowish-green gas and is highly water soluble, approximately 10 times more soluble in water than chlorine, particularly in cold water. Moreover, it remains in solution as a dissolved gas without hydrolyzing. Hence, it can be used in aqueous as well as gaseous forms. The advantages and limitations of using aqueous and gaseous ClO2 are summarized in Table 1.

Chlorine dioxide (ClO2) application in aqueous and gaseous form: advantages and disadvantages.

Aqueous application Gaseous application
Advantages (Praeger et al., 2018) Advantages (Sun et al., 2019)
Easy to handle, inexpensive Higher antimicrobial activity
It can be used in the form of spray, immerse or washing It can be applied as batch treatment or continuous treatment
Concentration and contact can be maintained High accessibility to microbes irrespective of surface barriers
Easy to adopt in industrial washing lines No water rinsing required after the treatment
It can impact microbial internalization
No issue of cross-contamination of wash water
Disadvantages (Praeger et al., 2018) Disadvantages (Sun et al., 2019)
Produce surface properties can affect ClO2 accessibility to microbes Needs onsite generation
Cross-contamination of wash water Needs technical knowledge
Water rinsing is required after the treatment laborious to perform, expensive
Residual moisture after the water rinsing can promote microbial growth Explosive at higher concentration
Not suitable for dried foods Challenging to maintain concentration and contact time
Relatively less effect on microbial internalization Difficult to implement at industry scale

Aqueous ClO2 solution can be used to spray, immerse, or wash fresh produce, as it ensures adequate ClO2 concentration and contact time, both of which are the determinants of its efficacy against pathogens. Moreover, aqueous ClO2 application is relatively easy to implement or adopt in the existing washing lines in food industries without modifying subsequent processes (Wu and Kim, 2007). However, water rinsing, an additional step, is required following aqueous ClO2 treatment, resulting in residual moisture on the produce surface that may stimulate microbial growth (Trinetta et al., 2011).

In contrast to aqueous ClO2, gaseous ClO2 is more effective against pathogens because of its higher potential to reach microbes irrespective of the surface irregularities of fresh produce (Han et al., 2001a). ClO2 is generally produced by the reaction of an acid with sodium chlorate or sodium chlorite and chlorine gas (Praeger et al., 2018). As gaseous ClO2 application does not require water, the risk of cross-contamination with recycled wash-water can be avoided. However, the major limitation of gaseous ClO2 application is its on-site production, as it cannot be compressed and stored or transported under pressure (EPA, 1999). Moreover, ClO2 production is laborious and expensive, and it is technically challenging to maintain a precise ClO2 concentration during gaseous treatment (Wu and Kim, 2007).

Alternatively, several packaging systems that can generate and release ClO2 have been developed. In these systems, materials that generate gaseous ClO2, including perforated sachets, pouches, tablets, films, and pads, are incorporated into the packaging system using different methods (Singh et al., 2021). Furthermore, for the development of an active packing material, factors, such as the release rate of the active material, its efficacy against microbes, and the maintenance of shelf-life of the product to be packed, are taken into consideration. These packaging systems are often designed to be used in combination with other technologies, such as modified atmosphere packaging (MAP).

 Modes of Chlorine Dioxide Action Antimicrobial Mechanisms

The antibacterial mechanism of ClO2 includes destabilization of the cell membrane, alteration of membrane permeability, and interruption of protein synthesis (Figure 1A). ClO2 reacts with oxygenated compounds and proteins in cell membranes, resulting in the disruption of cell metabolism (Praeger et al., 2018). Membrane damage in ClO2-exposed Bacillus subtilis spores inhibits their development after germination (Young and Setlow, 2003). Moreover, ClO2 oxidizes the exposed sulfhydryl groups of cell surface proteins, thereby causing membrane damage and increasing outer membrane permeability. Loss of permeability control, evident from the efflux of K+ ions, results in the destruction of transmembrane ionic gradient in Escherichia coli (Berg et al., 1986). Furthermore, loss of cell activity or cell death in ClO2-treated Pseudomonas aeruginosa and Staphylococcus aureus is correlated with the increased permeability of inner and outer cell membranes and the subsequent release of vital nuclear materials (Ofori et al., 2018). At higher concentrations, ClO2 induces accumulation of malondialdehyde (MDA) content, indicating the occurrence of membrane peroxidation (Bridges et al., 2020). However, previous studies based on transmission electron microscopy did not reveal significant morphological damage or cell lysis (Ofori et al., 2018; Bridges et al., 2020). Additionally, amino acids, including cysteine, tyrosine, tryptophan, histidine, and proline, are responsive to ClO2, with their order of reactivity from high to low, respectively (Sharma and Sohn, 2012).

Mechanisms of chlorine dioxide against bacteria (A) and viruses (B).

The virucidal mechanism of ClO2 varies depending on the composition and three-dimensional structure of viral proteins and nucleic acids (Figure 1B). Degradation of viral capsid proteins inhibits the attachment of ClO2-exposed bacteriophages to host cells (Ge et al., 2021). Similarly, the ClO2-mediated destruction of glycoproteins affects viral attachment to cell receptors and alters the life cycle of porcine reproductive and respiratory syndrome virus (Zhu et al., 2019). In addition, the denaturation of viral proteins has been reported to be involved in the inactivation of human rotavirus (Xue et al., 2013). ClO2 damages the 5’ non-coding region in the viral genome that is necessary for formation of new virus particles within the host cells (Li et al., 2004; Jin et al., 2013). Furthermore, RNA damage, in addition to protein damage, has been attributed to the inactivation of poliovirus (Simonet and Gantzer, 2006).

The fungicidal mechanism of ClO2 involves disruption of both the plasma and mitochondrial membranes (Zhang and Fu, 2018; Lin et al., 2021). ClO2 treatment causes ion leakage, inhibition of key enzyme activities in metabolic pathways, and alteration of cell structure in Saccharomyces cerevisiae (Zhu et al., 2013). Further, ClO2 induces membrane lipid peroxidation, which is evident by enhanced MDA levels in Penicillum expansum (Zhang and Fu, 2018).

 Potential Mechanisms Regulating Fresh Produce Quality

The mechanisms underlying the regulation of fresh produce quality by ClO2 include its impact on respiration rate and ethylene biosynthesis (Figure 2). ClO2-mediated inhibition of ethylene biosynthesis, brought about by the suppression of ethylene biosynthesis-related genes, including ACS2, ACO1, and ACO3 (Guo et al., 2013, 2014), alters the physiological and biochemical changes that occur during fruit maturation and senescence. Reduced respiration rate and transpiration delay the consumption of nutrients and water, which directly influences fruit firmness, mass loss, and softening (Chen and Zhu, 2011; Guo et al., 2013, 2014). The quality of fresh produce during storage depends on the correlation between cellular energy and redox status. For example, delayed senescence in ClO2-treated longan fruit has been reported to be associated with an altered redox state and increased cellular energy (Chumyam et al., 2016). Moreover, reduced microbial incidence in ClO2 treated produce leads to quality retention and shelf-life extension (Islam et al., 2017).

Potential mechanisms of chlorine dioxide regulating fresh produce quality. Dashed arrows indicate indirect effect.

 Effects of Chlorine Dioxide Treatment on Microbes Affecting Fresh Produce

Chlorine dioxide concentration and contact time are crucial in determining the efficacy of ClO2, which may also vary with the type of microorganism and fresh produce. The short-term and long-term efficacy of ClO2 in inhibiting the growth of preexisting or artificially inoculated microorganisms have been demonstrated in a wide variety of fresh produce (Tables 2, 3). Furthermore, some reports suggested that artificially inoculated human pathogens, such as E. coli, Salmonella spp., and Listeria monocytogenes, exhibit higher inactivation on fresh produce than natural microflora after ClO2 application (Praeger et al., 2018).

Effects of chlorine dioxide on short- and long-term reduction of microorganisms in vegetables.

Produce Microorganism Treatment conditions
 Log reductions
 Storage conditions References
Mode Concentration Duration Short-term Long-term
Lettuce Total aerobic bacteria Aq 50 ppm 10 min 1.77 0.9 8 days, 4°C Kim et al., 2007
Yeasts and molds 1.34 1.16
Coliforms 1.1 0.9
Lettuce Escherichia coli O157:H7 Aq 20 ppm 10 min 1.44 1.38 4 days, 4°C Kim et al., 2008
Salmonella 1.95 1.91
Listeria monocytogenes 1.2 0.99
Lettuce Escherichia coli O157:H7, L. monocytogenes Aq 3, 5 ppm 5 min 5.6 Unchanged 9 days, 4°C Rodgers et al., 2004
Lettuce Escherichia coli O157:H7 G 5 ppm 10 min 5 NA 7 days, 4°C Mahmoud and Linton, 2008
Salmonella enterica 5 NA
Mesophilic NA 2.7
Psychrotrophic NA 2
Yeast and molds NA 2.2
Spinach Escherichia coli O157:H7 Aq 100 ppm 5 min 2.6 0.13 7 days, 7°C Lee and Baek, 2008
Tomato Salmonella Aq 10 ppm 5 min 2.53 1.61 10 days, 4°C Song et al., 2011
Escherichia coli O157:H7 2.26 2.23
Tomato Alternaria alternata G 10 ppm 1 min 2.71 Completely inactivated 10 days, 25°C Trinetta et al., 2013
Stemphylium vesicarium 2.63 Completely inactivated
Tomato Salmonella enterica G 8 ppm 60 s 2.94 NA 28 days, 25°C Trinetta et al., 2010
10 ppm 120 s 3.86 NA
10 ppm 180 s 4.87 NA
Yeast and molds 1.57, 1.47, 1.54
Mesophilic bacteria 1.16, 2.81, 3.17
Tomato Listeria monocytogenes, Salmonella G 0.5 ppm 12 min >5 NA 28 days, 22°C Bhagat et al., 2010
Mesophilic NA 0.6
Yeast and molds NA 0.1
Tomato Escherichia coli G 3.5 ppm 14 days 2.9–4.7 3.08 14 days, 20°C Sun et al., 2017b
Alternaria alternata 1.6–4.0 2.85

Aq, aqueous; G, gaseous; NA, not available.

Effects of chlorine dioxide on short- and long-term reduction of microorganisms in fruits.

Produce Microorganism Treatment conditions
 Log reduction
 Storage conditions References
Mode Concentration Duration Short-term Long- term
Apples Escherichia coli O157:H7 Aq 3, 5 ppm 5 min 5.6 Unchanged 9 days, 4°C Rodgers et al., 2004
Listeria monocytogenes 5.6 Unchanged
Apples Salmonella G 4.1 ppm 6–25 min 4.21 NA 10 days, 10°C Sy et al., 2005b
Yeasts and molds 1.68 NA
Apple Alicyclobacillus acidoterrestris G 0.39 ppm 1 h 2.7 NA 7 days, 4°C Lee et al., 2006
0.50 ppm 2 h 3.7
0.60 ppm 3 h 4.5
Blueberry Salmonella enterica G 1.5 ppm NA 4.45 5.63 NA Annous et al., 2020
3 ppm 5.63
Blueberry Listeria monocytogenes Aq 1, 3, 5, 10, 15 ppm 10 s, 1, 5, 10, 20, 30 min; 1, 2 h 0.07–4.88 NA NA Wu and Kim, 2007
Pseudomonas aeruginos 0.15–4.48
Salmonella 0.12–3.32
Staphylococcus aureus, 0.21–4.56
Yersinia enterocolitica 0.18–3.69
Blueberries Total aerobic bacteria Aq 100 ppm 10 min 1.4–1.5 1.46 (20°), 1.14 (4°C) 12 days, 20 or 4°C Chun et al., 2013
Yeasts and molds 0.8–0.9 1.61 (20°), 0.35 (4°C)
Strawberry Escherichia coli O157:H7 G 0.5, 1, 1.5, 3, 5 ppm 10 min 4.6 NA 16 days, 22°C Mahmoud et al., 2007
Listeria monocytogenes 4.7 NA
Salmonella 4.3 NA
Mesophilic bacteria NA 3
Psychrotrophic bacteria 1.7
Yeast and mold 1.9
Strawberry Escherichia coli O157:H7 Aq 5 ppm 5 min 5.6 l Unchanged 9 days, 4°C Rodgers et al., 2004
Listeria monocytogenes 5.6 l Unchanged
Psychrotrophic 2.5 2.5
Lactic acid bacteria 1.5 1.7
Yeast and mold 1.1 1.1
Mulberry Mesophilic, Aq 20, 60, 80 ppm 5, 10, 15 min 2.4–2.8 2.0–2.6 14 days, -1°C Chen et al., 2011
Psychrotrophic 2.4–2.5 2.3–2.5
Lactic acid bacteria 1.4–1.5 1.5–1.7
Yeast and mold 1.0–1.1 0.9–1.1
Cantaloupe Escherichia coli O157:H7, G 5.0 ppm 5.5 min; 5 NA 12 days, 22°C Mahmoud et al., 2008
Listeria monocytogenes, Salmonella; 5 NA
Mesophilic 0.5, 1, 1.5, 3, 5 ppm 0, 2, 4, 6, 8, 10 min NA 2.4
Psychrotrophic bacteria, 4.1
Yeasts and molds 2.2
Cantaloupe Escherichia coli O157:H7, L. monocytogenes Aq 3, 5 ppm 5 min 5.6 Unchanged 9 days, 4°C Rodgers et al., 2004
Grape fruit Escherichia coli G 5 ppm 24 h Non-detectable NA 42 days, 10°C + 7 days, 20°C Sun et al., 2017a
Penicillium digitatum 60 ppm Non-detectable NA
Xanthomonas citri 14.5, 29 ppm Non-detectable NA
Total aerobic bacteria, NA 0.95
Yeast and mold NA 0.94
Peaches Salmonella, G 4.1 ppm 6–25 min 3.23 NA 10 days, 10°C Sy et al., 2005b
Yeasts and molds 2.68 NA

Aq, aqueous; G, gaseous; NA, not available.

 Short-Term Effects Vegetables

Washing leafy vegetables with aqueous ClO2 was effective in inactivating natural microflora. For instance, the initial populations of aerobic mesophilic, aerobic psychrotrophic, and lactic acid bacteria, yeast, and molds, in raw asparagus lettuce slices decreased by 1–3 log upon treatment with 100 ppm ClO2 for 20 min (Chen et al., 2010). Furthermore, exposure to 3 ppm ClO2 for 1 min reduced epiphytic microbiota on fresh-cut iceberg lettuce by 1–2 log (López-Gálvez et al., 2010). The efficacy of ClO2 against artificially inoculated pathogens, such as E. coli, Salmonella spp., and L. monocytogenes, has been extensively investigated in lettuce. A 2 min-long treatment with 100 or 200 ppm aqueous ClO2 in iceberg lettuce resulted in >1 log reduction in E. coli O157:H7 load (Keskinen et al., 2009). Similar results were obtained for S. typhimurium and L. monocytogenes inoculated on iceberg lettuce with lower ClO2 concentrations but longer exposure (10 min) (Kim et al., 2008). Moreover, Rodgers et al. (2004) observed >5 log reduction in the loads of E. coli O157:H7 and L. monocytogenes after ClO2 application (5 ppm for 5 min) on green leaf lettuce. Similar observations were made in whole heads of iceberg lettuce exposed to 5 ppm gaseous ClO2 for 15–20 min (Mahmoud and Linton, 2008). In spinach leaves, treatment with high ClO2 concentration for a short contact time (100 ppm for 5 min) or low ClO2 concentration with a long exposure time (10 ppm for 20 min) yielded approximately similar levels of pathogen reduction (Lee and Baek, 2008; Park and Kang, 2015b).

Several studies have investigated the disinfection of tomatoes using ClO2 (Praeger et al., 2018; Sun et al., 2019). For artificially inoculated human pathogens, 5–7 log reduction in microbial load has been observed with gaseous ClO2 concentrations < 1 ppm (Bhagat et al., 2010; Olanya et al., 2015; Netramai et al., 2016). For instance, a 12 min exposure to 0.5 ppm ClO2 resulted in >5 log reduction in Salmonella and L. monocytogenes loads in hydroponically grown tomatoes (Bhagat et al., 2010). With an increased exposure time (approximately 1 h), grape tomatoes exhibited >7 log reduction in the load of Salmonella spp., at 25°C (Netramai et al., 2016). Trinetta et al. (2010) evaluated the efficacy of short-term exposure of high ClO2 concentrations in the inactivation of S. enterica inoculated on tomatoes and observed that the initial populations (6 log) were reduced to 3 log, 2 log, and 1 log in response to 8 ppm ClO2 for 60 s, 10 ppm ClO2 for 120 s, and 10 ppm for 180 s, respectively. Previous studies suggest that the disinfection efficiency of ClO2 on tomatoes freshly spot-inoculated with Salmonella and Erwinia carotovora is higher than that on produce with desiccated inoculum (Pao et al., 2007). Moreover, tomato packaging with ClO2-generating materials, such as films, sachets, and pouches, is effective in achieving microbial reduction from 4 to 6 log to undetectable levels (Mahovic et al., 2007; Ray et al., 2013; Sun et al., 2017b; Zhou et al., 2018). Additionally, Trinetta et al. (2013) reported complete inhibition of the mycelial growth of Alternaria alternate and Stemphylium vesicarium using a 3 min-long ClO2 treatment. ClO2 efficiency has also been reported to increase with an increase in relative humidity and temperature (Park and Kang, 2015b,2018).

Antimicrobial efficiency of ClO2 has also been evaluated in other fresh vegetables. After ClO2 treatment, minimally processed carrots exhibited significantly decreased levels of mesophilic aerobic bacteria (1.9 log), psychrotrophs (1.7 log), lactic acid bacteria (2.6 log), and yeast (0.7 log) (Gomez-Lopez et al., 2007). Potato exposed to ClO2 for 5 h exhibited a 5 log and 6 log reduction in natural microflora and Pseudomonas aeruginosa, respectively (Wu and Rioux, 2010). ClO2 application for 30 min reduced the loads of E. coli O157:H7 or L. monocytogenes inoculated on surface-injured green peppers by 6.5 and 3.5 log, respectively (Han et al., 2000, 2001b). Similarly, ClO2 treatment effectively inactivated natural microbiota and inoculated Salmonella on the surface of chili peppers (Lee et al., 2018). Furthermore, disinfection of red chili pepper with ClO2 after hot-air drying significantly decreased Bacillus cereus spore populations below the detection limit (1.7 log) (Kim et al., 2017).

 Fruits

Aqueous ClO2 treatment (80 ppm for 15 min) yielded an approximately 1.5–3 log reduction in aerobic bacteria in mulberry (Chen et al., 2011). Similarly, a 10 min exposure to 100 ppm ClO2 significantly decreased the initial populations of natural microflora in blueberries (Chun et al., 2013). With gaseous ClO2 application (5.5 ppm), >5 log reduction in the load of artificially inoculated Salmonella spp., was observed in whole blueberries and strawberries (Annous et al., 2020). Similar results were observed for L. monocytogenes, E. coli O157:H7, yeast, and molds (Mahmoud et al., 2007; Popa et al., 2007; Wu and Kim, 2007). However, ClO2 efficacy was higher for Salmonella inoculated on blueberry skin tissues than for those inoculated on stem scar tissues (Sy et al., 2005a). Sun et al. (2014) reported an approximately 4 log reduction in the load of Colletotrichum acutatum on blueberries with ClO2 fumigation. Berries treated with ClO2, generated in a small chamber with acidified sodium chlorite solution, reduced Tulane virus populations by >1–3.3 log (Kingsley et al., 2018; Kingsley and Annous, 2019).

Previous studies have investigated the effects of various concentrations and exposure times of ClO2 on the populations of E. coli O157:H7 and L. monocytogenes on the skin surface, stem, and calyx cavities of apples. Although an exposure of 4.0 ppm ClO2 for 10 min resulted in a 5.5 log reduction in L. monocytogenes populations, treatment with 12.0 ppm ClO2 for 10 min, 7.2 ppm ClO2 for 20 min, or 4.8 ppm ClO2 for 30 min completely suppressed the bacterial population, which was initially inoculated on the skin (Du et al., 2002, 2003). Moreover, after 3 h of exposure to low ClO2-releasing sachets, the population of Alicyclobacillus acidoterrestris spores decreased to 4.5 log on apple surface (Lee et al., 2006). A 10 min-long fumigation with 0.5 ppm ClO2 on oranges resulted in >5 log reduction in Salmonella load (Bhagat et al., 2011). Gaseous ClO2, at concentrations 200−1,800 ppm, significantly lowered the incidence of green mold on citrus fruits, including kumquats, mandarins, and Peru oranges, and Penicillium digitatum on grapefruits (Liu et al., 2020). Furthermore, ClO2 treatment effectively reduced Xanthomonas citri contamination in both artificially and naturally contaminated citrus fruits (Behlau et al., 2021). Reports suggest that ClO2 treatment is more effective against E. coli inoculated on smooth non-stem-scar surfaces than on rough stem-scar areas (Pao and Davis, 1999). Additionally, X. citri on grapefruit surface requires a higher ClO2 concentration for complete inactivation than E. coli (Sun et al., 2017a).

 Long-Term Effects

Postharvest storage is essential for some types of fresh produce; however, microbial populations gradually increase during their storage. Hence, a strong disinfection method is required to ensure long-term protection of the treated produce. An initial reduction of microbial load is important for extending the microbiological shelf-life of fresh produce (Lin et al., 2021). Previous studies have reported different efficacies of ClO2 in inhibiting microbial growth during postharvest storage of produce (Praeger et al., 2018; Singh et al., 2021). A 20 min exposure to aqueous ClO2 inhibited the growth of natural microflora and prolonged the shelf-life of asparagus lettuce for 10 days (Chen et al., 2010). In ClO2-treated fresh produce, including apples, green leaf lettuce, cantaloupe, and strawberries, the populations of inoculated pathogens remained relatively unchanged, whereas the growth of natural microflora was significantly delayed after 9 days of storage at 4°C (Rodgers et al., 2004). In lettuce, ClO2 treatment (5.0 ppm for 10 min) maintained the populations of mesophilic and psychrotrophic bacteria, yeast, and mold under the detectable limit for 5 days at 4°C (Mahmoud and Linton, 2008). Similarly, ClO2-treated tomatoes exhibited significantly low microflora abundance during a storage period of 28 days; however, the efficacy of ClO2 varied with the exposure time and ClO2 concentration (Trinetta et al., 2010). Bhagat et al. (2010) demonstrated that treating tomato surface with 0.5 ppm ClO2 gas for 12 min delayed the growth of natural microflora and extended its shelf-life by 7 days during storage at 22°C. Furthermore, ClO2 treatment significantly delayed the development of white molds and black spots in Roma tomato wounds inoculated with S. vesicarium and A. alternate (Trinetta et al., 2013). Controlled release of ClO2 (4–6 ppm) reduced the loads of E. coli, Salmonella, and A. alternata on tomatoes by 3–5 log by the end of a 14 days-storage period (Sun et al., 2017b). Moreover, strawberries packed with ClO2-generating pads exhibited reduced growth of yeast and molds until 8 days of their 12 days-storage period at 2°C (Chiabrando et al., 2018). Similarly, ClO2 treatment reduced total aerobic bacterial and yeast and mold counts by 0.95 and 0.94 log, respectively, in grape fruit after 6 weeks of storage at 10°C (Sun et al., 2017a).

By contrast, ClO2 exhibits no long-term effects on reducing microbial contamination despite its initial effect. Treating cucumbers with various concentrations of ClO2, ranging from 20 to 125 ppm, did not delay mold growth during storage (Praeger et al., 2018). Although ClO2 treatment, in combination with MAP, was effective in controlling microflora on mungbean sprouts during storage, ClO2 treatment alone could not reduce the incidences of S. typhimurium and L. monocytogenes (Jin and Lee, 2007). ClO2 treatment of fresh-cut lettuce packed in MAP did not inhibit the growth of yeast during storage (López-Gálvez et al., 2010). However, 3 and 5 ppm ClO2 were more effective against L. monocytogenes than yeasts and molds during cold storage (Rodgers et al., 2004).

 Effects of Chlorine Dioxide Treatment on the Postharvest Quality of Fresh Produce Color

Color is one of the fundamental characteristics that determines the visual quality and acceptability of fresh produce. Depending on the concentration, ClO2 differentially affects the appearance of treated fresh produce (Table 4). However, previous studies suggest that ClO2 has no effect on the color of fresh produce; ClO2 exposure had no effect on Hunter L, a, and b values of tomatoes, spinach, and lettuce (Kim et al., 2007; Song et al., 2011; Hassenberg et al., 2014; Park and Kang, 2015a). Similarly, treatment with 0.5 ppm ClO2 gas for 12 min did not significantly affect the color of orange peel (Bhagat et al., 2011). Furthermore, the appearance of blueberries was not affected by long-term ClO2 exposure (2–12 h) (Popa et al., 2007; Wu and Kim, 2007). By contrast, higher concentrations of ClO2 result in the bleaching of fresh produce. For example, strawberries treated with ClO2 underwent white bleaching after 8 days of storage at 2°C (Chiabrando et al., 2018). Oxidation of oligosaccharides, such as cellulose and hemicellulose, and chlorophyll, has been hypothesized as the possible cause of bleaching in fresh produce (Singh et al., 2002; Chen and Zhu, 2011).

Effects of chlorine dioxide on color and visual quality of fresh produce.

Produce Mode ClO2 concentration Duration Storage ClO2 effect References
Color
Lettuce Aq 0, 5, 10, 20 ppm 10 min 4 days, 4°C Unaffected Kim et al., 2008
Lettuce Aq 50 ppm 10 min 8 days, 4°C Unaffected Kim et al., 2007
Lettuce Aq 10, 40, 100 ppm 5, 10, 20 min 14 days, 4°C Delayed degradation of color Chen et al., 2010
Lettuce G 0.5, 5.0 ppm 2, 10 min 7 days, 4°C Leaf discoloration Mahmoud and Linton, 2008
Lettuce G 1.4 ppm 5.4–10.5 min 10 days, 10°C Slight leaf browning Sy et al., 2005b
2.7 ppm 10.4–20.0 min Leaf browning
4.1 ppm 20.5–30.8 min Neaf browning
Spinach G 1–30 ppm 20 min 7 days, 4°C Unaffected Park and Kang, 2015b
50 ppm Hiher L* and b* values
Cabbage G 1.4 ppm 5.4–10.5 min 10 days, 10°C Slight browning Sy et al., 2005b
2.7 ppm 10.4–20.0 min Leaf browning
4.1 ppm 20.5–30.8 min Leaf browning
Tomato Aq 10 ppm 5 min 10 days, 4°C Unaffected Song et al., 2011
50 ppm 20 min Discoloration
Tomato G 8 ppm 60 s 25°C, 28 days Unaffected Trinetta et al., 2010
Tomato 10 ppm 120, 180 s 25°C, 28 days Skin wrinkling Trinetta et al., 2010
Tomato G 0.5 ppm 12 min 28 days, 22°C Unaffected Bhagat et al., 2010
Tomato G 1.4 ppm 6 min 10 days, 21°C Unaffected Sy et al., 2005b
2.7 ppm 12 min Unaffected
4.1 ppm 25 min Unaffected
Carrot G 1.4 ppm 5.4–10.5 min 10 days, 10°C Slight whitening in the color Sy et al., 2005b
2.7 ppm 10.4–20.0 min Whitening in the color
4.1 ppm 20.5–30.8 min Whitening in the color
Onions G 1.4 ppm 5.4 min 12 or 20 days, 21°C Unaffected Sy et al., 2005b
2.7 ppm 10.4 min Unaffected
4.1 ppm 20 min . Unaffected
Apple G 1.4 ppm 6 min 41 days, 21°C Unaffected
2.7 ppm 12 min Unaffected
4.1 ppm 25 min Small brown spots on the skin
Cantaloupe G 0.5–5.0 mg/L 0–10 min 12 days, 22°C Unaffected Mahmoud et al., 2008
Strawberry G 0.5–5 ppm 10 min 16 days, 4°C Unaffected Mahmoud et al., 2007
29 ppm Peel browning
Strawberry G NA NA 3 days, 4°C + 2 days at 20°C/12 days, 2°C Unaffected Chiabrando et al., 2018
12 days, 2°C Unaffected
Strawberry Aq 5 ppm NA 3 weeks, 4°C Maintained L and a values Aday and Caner, 2011
Decreased L and a values
Peaches G 1.4 ppm 5.4 min 10 days, 21°C Browning Sy et al., 2005b
2.7 ppm 10.4 min . Browning
4.1 ppm 20 min . Browning
Visual quality
Tomato G 5 ppm 12 h 20 days, 5°C Delayed color development Islam et al., 2017
Apple G 0.39–0.60 ppm 1–3 h 7 days, 4°C Unaffected Lee et al., 2006
1.78–2.69 ppm 1–3 h Black spots on the fruit surface
4.32–6.55 ppm 1–3 h Black spots on the fruit surface
Grapefruit G 14.5 ppm 10 days 42 days, 10°C + 7 days, 20°C Maintained Sun et al., 2017a
29 ppm Peel browning

Aq, aqueous; G, gaseous; NA, not available.

Chlorine dioxide has been reported to differentially affect enzymatic browning of fresh produce, resulting from the oxidation of phenols to o-quinones that is catalyzed by polyphenol oxidase (PPO; Altunkaya and Gökmen, 2009) during postharvest handling and processing. In grapes, repeated application of ClO2 during storage significantly decreased rachis browning (Chen et al., 2018). Reduced browning in a variety of fresh produce, such as fresh-cut asparagus lettuce, and apples, is associated with decreased PPO activity (Fu et al., 2007; Chen et al., 2010). This can be attributed to the oxidation of disulfide bonds and amino acids at the active site of PPO by ClO2 (Fu et al., 2007). By contrast, ClO2 treatment may also cause browning of fresh produce. For example, ClO2 treatment resulted in rapid color change in spinach leaves, browning of grapefruit, cabbage, lettuce, peaches, and apples (Sy et al., 2005b; Lee et al., 2006; Mahmoud and Linton, 2008; Park and Kang, 2015a; Sun et al., 2017a).

 Firmness

Firmness, another important quality-determining characteristic, influences consumer appeal and the commercial value of fresh produce. Effect of ClO2 treatment on firmness and weight loss of fresh produce is summarized in Table 5. ClO2 treatment retains the firmness of several fresh fruits, such as strawberries, plums, apricots, and mangoes, during postharvest storage (Aday and Caner, 2011; Chen and Zhu, 2011; Zhang et al., 2019). Furthermore, controlled-release of ClO2 gas has been reported to regulate the firmness of non-inoculated and E. coli- and C. acutatum-inoculated berries during storage (Sun et al., 2014).

Effects of chlorine dioxide on firmness and weight loss of fresh produce.

Produce Mode ClO2 concentration Duration Weight loss Firmness Storage References
Spinach G 1–30 ppm 20 min Unaffected 7 days, 4°C Park and Kang, 2015b
Spinach G 1–50 ppm 20 min Unaffected 7 days, 4°C Park and Kang, 2015b
Grape tomatoes G 2–3.5 ppm 14 days Reduced Increased 14 days, 20°C Sun et al., 2017b
Grape tomatoes G 2, 4, 6, 8 ppm 14 days Reduced Increased 14 days, 20°C Sun et al., 2017c
Cherry tomatoes G 2, 4, 6, 8 ppm 14 days Reduced Maintained 14 days, 20°C Sun et al., 2017c
Tomato G 10 ppm 120, 180 s Skin wrinkling 25°C, 28 days Trinetta et al., 2010
Tomato G 5 ppm 12 h Reduced Increased 20 days, 5°C Islam et al., 2017
Strawberry Aq 5 ppm NA Reduced 3 weeks, 4°C Aday and Caner, 2011
10 ppm Increased
Blueberry G 1–2.5 ppm 9 days Maintained 9 days, 10°C Sun et al., 2014

Aq, aqueous; G, gaseous; NA, not available.

After harvesting, respiration and transpiration continue in fresh produce, and carbohydrate and water reserves are continually consumed without replacement, leading to progressive loss of turgidity and weight during storage. Fruit moisture and weight loss are associated with decreased fruit firmness, shrinking, and shriveling (Paniagua et al., 2013; Lufu et al., 2020). However, ClO2 reduces the rate of water loss in the ClO2-treated produce (Guo et al., 2014; Wang et al., 2014). The application of ClO2 at low concentrations for long durations in active packaging material has been shown to improve fruit firmness and reduce water loss (Guo et al., 2014).

Less weight loss in ClO2-treated berries is associated with 50% closed stomata during storage at low temperatures (Wang et al., 2014). In general, fruit ripening is associated with a climacteric increase in ethylene production and extensive modifications in cell wall polysaccharides. ClO2 delays the increase in respiration rate and ethylene biosynthesis, resulting in delayed ripening that further leads to delayed fruit softening (Chen and Zhu, 2011; Guo et al., 2013, 2014). ClO2 may also alter tissue metabolism by oxidizing cell constituents, thereby leading to changes in respiration, and, in turn, inhibiting weight loss and maintaining fruit firmness (Gomez-Lopez et al., 2008).

 Sensory Properties

Previous studies have reported that ClO2 treatment can retain the sensory properties of fresh produce. Effect of ClO2 treatment on sensory properties of fresh produce is summarized in Table 6. For example, gaseous ClO2 treatment (4.1 ppm) did not compromise the sensory qualities of blueberries, strawberries, and raspberries stored for 10 days at 8°C (Sy et al., 2005a). Similar results were obtained for fresh-cut cabbage, carrot, and iceberg lettuce treated with 3–5 ppm ClO2 (Rodgers et al., 2004; Sy et al., 2005b; López-Gálvez et al., 2010). Moreover, ClO2 treatment positively affects the composition of volatile compounds and free amino acids in citrus fruits, resulting in the retention of their distinct flavor (Liu et al., 2020). Furthermore, ClO2-treated plums maintain high sensory properties during storage (Chen and Zhu, 2011). Few studies revealed that the sensory properties of fresh produce can be improved by ClO2 application. For instance, ClO2-treated strawberries, blueberries, and mulberries exhibited better sensory scores than the untreated controls (Jin and Lee, 2007; Wu and Kim, 2007; Chen et al., 2011; Chun et al., 2013). Nonetheless, 20 ppm ClO2 significantly affected the sensory properties of lettuce and cabbage (Gomez-Lopez et al., 2008).

Effects of chlorine dioxide on sensory properties of fresh produce.

Produce Mode ClO2 concentration Duration Storage Sensory property References
Lettuce Aq 3 ppm 1 min 3 days, 4°C + 7 days, 8°C Unaffected López-Gálvez et al., 2010
Lettuce Aq 50 ppm 10 min 8 days, 4°C Unaffected Kim et al., 2007
Lettuce Aq 3, 5 ppm 48 h, 4°C Unaffected Rodgers et al., 2004
Lettuce Aq 10, 40, 100 ppm 5, 10, 20 min 14 days, 4°C Unaffected Chen et al., 2010
Lettuce G 1.4 ppm 5.4–10.5 min 10 days, 10°C Decreased Sy et al., 2005b
Cabbage G 1.4 ppm 5.4–10.5 min 10 days, 10°C Decreased Sy et al., 2005b
Carrot G 1.4 ppm 5.4–10.5 min 10 days, 10°C Decreased Sy et al., 2005b
Tomato G 1.4 ppm 6 min 10 days, 21°C Unaffected Sy et al., 2005b
Onions G 1.4 ppm 5.4 min 12 or 20 days, 21°C Unaffected Sy et al., 2005b
Apple Aq 3, 5 ppm 48 h, 4°C Unaffected Rodgers et al., 2004
Strawberry Aq 3, 5 ppm 48 h, 4°C Unaffected Rodgers et al., 2004
Strawberry Aq 5 ppm 3 weeks, 4°C Maintained Aday and Caner, 2011
Maintained
Cantaloupe Aq 3, 5 ppm 48 h, 4°C Unaffected Rodgers et al., 2004
Blueberry G 4 ppm 12 h Overnight, 4°C Improved Popa et al., 2007
Apple G 1.4 ppm 6 min Unaffected
Peaches G 1.4 ppm 5.4 min 10 days, 21°C Decreased Sy et al., 2005b
2.7 ppm 10.4 min Decreased
4.1 ppm 20 min Decreased
Grapefruit G 14.5 ppm 10 days 42 days, 10°C + 7 days, 20°C Maintained Sun et al., 2017a

Aq, aqueous; G, gaseous.

 Chlorine Dioxide Application: Efficacy and Limitations

Because of its high oxidative capacity (2.5-fold that of chlorine), ClO2 is effective in microbial inactivation at concentration as low as 0.1 ppm with minimal contact time (Praeger et al., 2018). Most importantly, ClO2 is effective against both Gram-positive and Gram-negative bacteria, whereas molds and yeasts showed intermediate tolerance (Yoon and Lee, 2018; Sun et al., 2019). Additionally, ClO2 does not react with organic matter to form carcinogenic by-products such as trihalomethanes which makes ClO2 to be effective over a wide pH range (Praeger et al., 2018). In the United States, a maximum 3 ppm of ClO2 is allowed for fresh produce treatment. In Europe, rinsing with potable water is necessary following the ClO2 treatment (Praeger et al., 2018).

Comparison of disinfection efficacy of various sanitizers revealed that gaseous ClO2, hydrostatic pressure and electrolyzed oxidizing water were more effective in microbial inactivation than other sanitizers. The average microbial reductions of ClO2 gas, hydrostatic pressure and electrolyzed oxidizing water were 4.07, 3.94, and 3.01 log, respectively (Yoon and Lee, 2018). On the other hand, the average microbial inactivation of aqueous ClO2 (1.49 log) was less than gaseous ClO2, however, it was still higher than chlorine-based disinfectants (1.12 log) (Yoon and Lee, 2018). Higher antimicrobial activity of gaseous ClO2 may attribute to its easier accessibility to microbes located in the unreachable parts the fresh produce. Moreover, ClO2 gas can readily diffuse into the tissues of fresh produce, hence, it may inactivate internalized microbes (Yoon and Lee, 2018). However, handling with gaseous ClO2 is inconvenient as it needs to be produced onsite. Moreover, it is expensive and requires technical expertise.

The major limitations of ClO2 for practical applications include it may not be effective at permitted concentrations; it may affect quality of treated fresh produce in some instances. Since ClO2 is highly explosive and toxic to humans at higher concentrations, it is challenging to implement this treatment technology at industry scale.

 Conclusion and Future Perspectives

Chlorine dioxide application, in gaseous and aqueous forms, has been demonstrated to be effective in controlling microbial growth and retaining the quality of fresh produce, however, it is largely depending upon the respective produce type and treatment conditions. Gaseous ClO2 is more effective than the aqueous form. Nevertheless, although aqueous ClO2 solutions may be easy to use, they require an additional washing step. ClO2, whether in gaseous or aqueous form, destabilizes cell membranes, alters membrane permeability, and interrupts protein synthesis in microbes, along with influencing ethylene biosynthesis and respiration rate in fresh produce, which are crucial for maintaining the quality of fresh produce. In general, initial reduction in microbial load significantly affects microbial contamination during storage of fresh produce, thereby resulting in an extended shelf-life. Previous studies suggest that ClO2 concentration and exposure time are crucial in determining the efficacy of ClO2 against microbes, but a holistic approach is required to unravel the mechanisms underlying the regulation of fresh produce quality by ClO2.

Our review showed that current research on disinfection by ClO2 has mainly focused on the bactericidal effects of ClO2; recently, studies on antifungal and antiviral effects of ClO2, are gaining attention. Currently, the efficacy of ClO2 has been mostly tested at the laboratory level, thus, highlighting the need for industrial-level testing for various types of fresh produce. Disposition and chemical fate of ClO2 gas on treated fresh produce are not well understood; therefore, further studies should focus on this dimension, which has been largely neglected in studies on ClO2 disinfection. Moreover, this review did not assess the different methods of ClO2 generation and the efficacy of ClO2 in combination with other technologies for postharvest quality and microbial safety of fresh produce.

 Author Contributions

M-HP: supervision. SM and M-HP: conceptualization, writing–original draft preparation, contributed to the article, and approved the submitted version.

 Conflict of Interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

 Publisher’s Note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.

 Funding

This study was funded by the Cooperative Research Program for Agriculture, Science, and Technology (Project No. PJ01502903) in the Rural Development Administration of the Republic of Korea.

 References Aday M. S. Caner C. (2011). The Applications of ‘active packaging and chlorine dioxide’ for extended shelf life of fresh strawberries. Packaging Technol. Sci. 24 123–136. 10.1002/pts.918 Altunkaya A. Gökmen V. (2009). Effect of various anti-browning agents on phenolic compounds profile of fresh lettuce (L. sativa). Food Chem. 117 122–126. 10.1016/j.foodchem.2009.03.085 Annous B. A. Buckley D. Burke A. (2020). Evaluation of Chlorine Dioxide Gas against Four Salmonella enterica Serovars Artificially Contaminated on Whole Blueberries. J. Food Prot. 83 412–417. 10.4315/0362-028X.JFP-19-452 32050031 Behlau F. Paloschi A. Marin T. G. S. Santos T. A. Ferreira H. Nascimento L. M. D. (2021). Chlorine dioxide, peroxyacetic acid, and calcium oxychloride for post-harvest decontamination of citrus fruit against Xanthomonas citri subsp. citri, causal agent of citrus canker. Crop Protect. 146:105679. 10.1016/j.cropro.2021.105679 Berg J. D. Roberts P. V. Matin A. (1986). Effect of chlorine dioxide on selected membrane functions of Escherichia coli. J. Appl. Bacteriol. 60 213–220. 10.1111/j.1365-2672.1986.tb01075.x 3519558 Bhagat A. Mahmoud B. S. Linton R. H. (2010). Inactivation of Salmonella enterica and Listeria monocytogenes inoculated on hydroponic tomatoes using chlorine dioxide gas. Foodborne Pathog. Dis. 7 677–685. 10.1089/fpd.2009.0466 20353288 Bhagat A. Mahmoud B. S. Linton R. H. (2011). Effect of chlorine dioxide gas on Salmonella enterica inoculated on navel orange surfaces and its impact on the quality attributes of treated oranges. Foodborne Pathog. Dis. 8 77–85. 10.1089/fpd.2010.0622 20932090 Bridges D. F. Lacombe A. Wu V. C. H. (2020). Integrity of the Escherichia coli O157:H7 Cell Wall and Membranes After Chlorine Dioxide Treatment. Front. Microbiol. 11:888. 10.3389/fmicb.2020.00888 32499765 Buzby J. C. Farah-Wells H. Hyman J. (2014). The Estimated Amount, Value, and Calories of Postharvest Food Losses at the Retail and Consumer Levels in the United States. USDA ERS Econom. Informat. Bull. Number 121:2501659. 10.2139/ssrn.2501659 CDC (2018). National Outbreak Reporting System (NORS). Atlanta, GA: CDC. Chacha J. S. Zhang L. Ofoedu C. E. Suleiman R. A. Dotto J. M. Roobab U. (2021). Revisiting Non-Thermal Food Processing and Preservation Methods-Action Mechanisms, Pros and Cons: A Technological Update (2016-2021). Foods 10:foods10061430. 10.3390/foods10061430 34203089 Chen S. Wang H. Wang R. Fu Q. Zhang W. (2018). Effect of gaseous chlorine dioxide (ClO2) with different concentrations and numbers of treatments on controlling berry decay and rachis browning of table grape. J. Food Proces. Preservat. 42:13662. 10.1111/jfpp.13662 Chen Z. Zhu C. (2011). Combined effects of aqueous chlorine dioxide and ultrasonic treatments on postharvest storage quality of plum fruit (Prunus salicina L.). Postharv. Biol. Technol. 61 117–123. 10.1016/j.postharvbio.2011.03.006 Chen Z. Zhu C. Han Z. (2011). Effects of aqueous chlorine dioxide treatment on nutritional components and shelf-life of mulberry fruit (Morus alba L.). J. Biosci. Bioeng. 111 675–681. 10.1016/j.jbiosc.2011.01.010 21306948 Chen Z. Zhu C. Zhang Y. Niu D. Du J. (2010). Effects of aqueous chlorine dioxide treatment on enzymatic browning and shelf-life of fresh-cut asparagus lettuce (Lactuca sativa L.). Postharv. Biol. Technol. 58 232–238. 10.1016/j.postharvbio.2010.06.004 Chiabrando V. Giuggioli N. Maghenzani M. Peano C. Giacalone G. (2018). Improving Storability of Strawberries with Gaseous Chlorine Dioxide in Perforated Clamshell Packaging. Polish J. Food Nutrit. Sci. 68 141–148. 10.1515/pjfns-2017-0024 Chumyam A. Shank L. Uthaibutra J. Saengnil K. (2016). Effects of chlorine dioxide on mitochondrial energy levels and redox status of ‘Daw’ longan pericarp during storage. Postharv. Biol. Technol. 116 26–35. 10.1016/j.postharvbio.2016.01.002 Chun H. H. Yu D. J. Song K. B. (2013). Effects of combined nonthermal treatment on microbial growth and the quality of minimally processed yam (Dioscorea japonicaThunb) during storage. Int. J. Food Sci. Technol. 48 334–340. 10.1111/j.1365-2621.2012.03191.x Deng L. Z. Mujumdar A. S. Pan Z. Vidyarthi S. K. Xu J. Zielinska M. (2020). Emerging chemical and physical disinfection technologies of fruits and vegetables: a comprehensive review. Crit. Rev. Food Sci. Nutr. 60 2481–2508. 10.1080/10408398.2019.1649633 31389257 Du J. Han Y. Linton R. H. (2002). Inactivation by chlorine dioxide gas (ClO2) of Listeria monocytogenes spotted onto different apple surfaces. Food Microbiol. 19 481–490. 10.1006/fmic.2002.0501 Du J. Han Y. Linton R. H. (2003). Efficacy of chlorine dioxide gas in reducing Escherichia coli O157:H7 on apple surfaces. Food Microbiol. 20 583–591. 10.1016/s0740-0020(02)00129-6 EPA (1999). Alternative disinfectants and oxidants, guidance manual. Washington, D.C: Environmental Protection Agency. European Food Safety Authority (2021). The European Union One Health 2019 Zoonoses Report. EFSA J. 19:e06406. 10.2903/j.efsa.2021.6406 33680134 FAO (2011). Global food losses and food waste. Rome: FAO. FDA (2008). Guidance for industry: guide to minimize microbial food safety hazards for fresh fruits and vegetables. Silver Spring: FDA. Fu Y. Zhang K. Wang N. Du J. (2007). Effects of aqueous chlorine dioxide treatment on polyphenol oxidases from Golden Delicious apple. LWT Food Sci. Technol. 40 1362–1368. 10.1016/j.lwt.2006.11.001 Ge Y. Zhang X. Shu L. Yang X. (2021). Kinetics and Mechanisms of Virus Inactivation by Chlorine Dioxide in Water Treatment: A Review. Bull. Environ. Contam. Toxicol. 106 560–567. 10.1007/s00128-021-03137-3 33629148 Gomez-Lopez V. M. Devlieghere F. Ragaert P. Debevere J. (2007). Shelf-life extension of minimally processed carrots by gaseous chlorine dioxide. Int. J. Food Microbiol. 116 221–227. 10.1016/j.ijfoodmicro.2006.12.008 17306398 Gomez-Lopez V. M. Ragaert P. Jeyachchandran V. Debevere J. Devlieghere F. (2008). Shelf-life of minimally processed lettuce and cabbage treated with gaseous chlorine dioxide and cysteine. Int. J. Food Microbiol. 121 74–83. 10.1016/j.ijfoodmicro.2007.11.036 18077040 Guo Q. Lv X. Xu F. Zhang Y. Wang J. Lin H. (2013). Chlorine dioxide treatment decreases respiration and ethylene synthesis in fresh-cut ‘Hami’ melon fruit. Int. J. Food Sci. Technol. 48 1775–1782. 10.1111/ijfs.12149 Guo Q. Wu B. Peng X. Wang J. Li Q. Jin J. (2014). Effects of chlorine dioxide treatment on respiration rate and ethylene synthesis of postharvest tomato fruit. Postharv. Biol. Technol. 93 9–14. 10.1016/j.postharvbio.2014.01.013 Han Y. Floros J. D. Linton R. H. Nielsen S. S. Nelson P. E. (2001a). Response surface modeling for the inactivation of Escherichia coli O157:H7 on green peppers (Capsicum annuum L.) by chlorine dioxide gas treatments. J. Food Prot. 64 1128–1133. 10.4315/0362-028x-64.8.1128 11510647 Han Y. Linton R. H. Nielsen S. S. Nelson P. E. (2001b). Reduction of Listeria monocytogenes on green peppers (Capsicum annuum L.) by gaseous and aqueous chlorine dioxide and water washing and its growth at 7 degrees C. J. Food Prot. 64 1730–1738. 10.4315/0362-028x-64.11.1730 11726151 Han Y. Sherman D. M. Linton R. H. Nielsen S. S. Nelson P. E. (2000). The effects of washing and chlorine dioxide gas on survival and attachment of Escherichia coli O157: H7 to green pepper surfaces. Food Microbiol. 17 521–533. 10.1006/fmic.2000.0343 Hassenberg K. Herppich W. B. Praeger U. (2014). Chlorine dioxide for the reduction of human pathogens in lettuce washing process. Landtechnik 69 185–189. Islam M. Z. Mahmuda A. M. Jong M. P. Il-Seop K. Ho-Min K. (2017). Chlorine dioxide gas retain postharvest quality and shelf life of tomato during modified atmosphere packaging storage. AGRIVITA J. Agricult. Sci. 39 10.17503/agrivita.v39i3.1454 Jin H. H. Lee S. Y. (2007). Combined effect of aqueous chlorine dioxide and modified atmosphere packaging on inhibiting Salmonella typhimurium and Listeria monocytogenes in mungbean sprouts. J. Food Sc.i 72 M441–M445. 10.1111/j.1750-3841.2007.00555.x 18034740 Jin M. Shan J. Chen Z. Guo X. Shen Z. Qiu Z. (2013). Chlorine dioxide inactivation of enterovirus 71 in water and its impact on genomic targets. Environ. Sci. Technol. 47 4590–4597. 10.1021/es305282g 23560857 Joshi K. Mahendran R. Alagusundaram K. Norton T. Tiwari B. K. (2013). Novel disinfectants for fresh produce. Trends Food Sci. Technol. 34 54–61. 10.1016/j.tifs.2013.08.008 Keskinen L. A. Burke A. Annous B. A. (2009). Efficacy of chlorine, acidic electrolyzed water and aqueous chlorine dioxide solutions to decontaminate Escherichia coli O157:H7 from lettuce leaves. Int. J. Food Microbiol. 132 134–140. 10.1016/j.ijfoodmicro.2009.04.006 19428137 Kim S. Lee H. Ryu J. H. Kim H. (2017). Inactivation of Bacillus cereus Spores on Red Chili Peppers Using a Combined Treatment of Aqueous Chlorine Dioxide and Hot-Air Drying. J. Food Sci. 82 1892–1897. 10.1111/1750-3841.13771 28631818 Kim Y. J. Lee S. H. Song K. B. (2007). Effect of aqueous chlorine dioxide treatment on the microbial growth and qualities of iceberg lettuce during storage. J. Appl. Biol. Chem. 50 239–243. Kim Y. J. Lee S. H. Park J. Park J. Chung M. Kwon K. (2008). Inactivation of Escherichia coli O157:H7, Salmonella typhimurium, and Listeria monocytogenes on stored iceberg lettuce by aqueous chlorine dioxide treatment. J. Food Sci. 73 M418–M422. 10.1111/j.1750-3841.2008.00940.x 19021812 Kingsley D. H. Annous B. A. (2019). Evaluation of Steady-State Gaseous Chlorine Dioxide Treatment for the Inactivation of Tulane virus on Berry Fruits. Food Environ. Virol. 11 214–219. 10.1007/s12560-019-09382-4 30949936 Kingsley D. H. Perez-Perez R. E. Niemira B. A. Fan X. (2018). Evaluation of gaseous chlorine dioxide for the inactivation of Tulane virus on blueberries. Int. J. Food Microbiol. 273 28–32. 10.1016/j.ijfoodmicro.2018.01.024 29558681 Lee H. Beuchat L. R. Ryu J. H. Kim H. (2018). Inactivation of Salmonella typhimurium on red chili peppers by treatment with gaseous chlorine dioxide followed by drying. Food Microbiol. 76 78–82. 10.1016/j.fm.2018.04.016 30166193 Lee S. Y. Baek S. Y. (2008). Effect of chemical sanitizer combined with modified atmosphere packaging on inhibiting Escherichia coli O157:H7 in commercial spinach. Food Microbiol. 25 582–587. 10.1016/j.fm.2008.02.003 18456113 Lee S. Y. Dancer G. I. Chang S. S. Rhee M. S. Kang D. H. (2006). Efficacy of chlorine dioxide gas against Alicyclobacillus acidoterrestris spores on apple surfaces. Int. J. Food Microbiol. 108 364–368. 10.1016/j.ijfoodmicro.2005.11.023 16466821 Li J. W. Xin Z. T. Wang X. W. Zheng J. L. Chao F. H. (2004). Mechanisms of inactivation of hepatitis A virus in water by chlorine dioxide. Water Res. 38 1514–1519. 10.1016/j.watres.2003.12.021 15016528 Lin X. Chen G. Jin T. Z. Wen M. Wu J. Wen J. (2021). Extension of shelf life of semi-dry longan pulp with gaseous chlorine dioxide generating film. Int. J. Food Microbiol. 337:108938. 10.1016/j.ijfoodmicro.2020.108938 33166912 Liu X. Jiao W. Du Y. Chen Q. Su Z. Fu M. (2020). Chlorine Dioxide Controls Green Mold Caused by Penicillium digitatum in Citrus Fruits and the Mechanism Involved. J. Agric. Food Chem. 68 13897–13905. 10.1021/acs.jafc.0c05288 33146520 López-Gálvez F. Allende A. Truchado P. Martínez-Sánchez A. Tudela J. A. Selma M. V. (2010). Suitability of aqueous chlorine dioxide versus sodium hypochlorite as an effective sanitizer for preserving quality of fresh-cut lettuce while avoiding by-product formation. Postharv. Biol. Technol. 55 53–60. 10.1016/j.postharvbio.2009.08.001 Lufu R. Ambaw A. Opara U. L. (2020). Water loss of fresh fruit: Influencing pre-harvest, harvest and postharvest factors. Sci. Horticult. 272:109519. 10.1016/j.scienta.2020.109519 Mahmoud B. S. Linton R. H. (2008). Inactivation kinetics of inoculated Escherichia coli O157:H7 and Salmonella enterica on lettuce by chlorine dioxide gas. Food Microbiol. 25 244–252. 10.1016/j.fm.2007.10.015 18206766 Mahmoud B. S. Bhagat A. R. Linton R. H. (2007). Inactivation kinetics of inoculated Escherichia coli O157:H7, Listeria monocytogenes and Salmonella enterica on strawberries by chlorine dioxide gas. Food Microbiol. 24 736–744. 10.1016/j.fm.2007.03.006 17613371 Mahmoud B. S. Vaidya N. A. Corvalan C. M. Linton R. H. (2008). Inactivation kinetics of inoculated Escherichia Coli O157:H7, Listeria monocytogenes and Salmonella Poona on whole cantaloupe by chlorine dioxide gas. Food Microbiol. 25 857–865. 10.1016/j.fm.2008.05.009 18721673 Mahovic M. J. Tenney J. D. Bartz J. A. (2007). Applications of Chlorine Dioxide Gas for Control of Bacterial Soft Rot in Tomatoes. Plant Dis. 91 1316–1320. 10.1094/PDIS-91-10-1316 30780519 Netramai S. Kijchavengkul T. Sakulchuthathip V. Rubino M. (2016). Antimicrobial efficacy of gaseous chlorine dioxide against Salmonella enterica Typhimurium on grape tomato (Lycopersicon esculentum). Int. J. Food Sci. Technol. 51 2225–2232. 10.1111/ijfs.13209 Ofori I. Maddila S. Lin J. Jonnalagadda S. B. (2018). Chlorine dioxide inactivation of Pseudomonas aeruginosa and Staphylococcus aureus in water: The kinetics and mechanism. J. Water Process Engine. 26 46–54. 10.1016/j.jwpe.2018.09.001 Olanya O. M. Annous B. A. Taylor J. (2015). Effects of Pseudomonas chlororaphis and gaseous chlorine dioxide on the survival of Salmonella entericaon tomatoes. Int. J. Food Sci. Technol. 50 1102–1108. 10.1111/ijfs.12748 Paniagua A. C. East A. R. Hindmarsh J. P. Heyes J. A. (2013). Moisture loss is the major cause of firmness change during postharvest storage of blueberry. Postharv. Biol. Technol. 79 13–19. 10.1016/j.postharvbio.2012.12.016 Pao S. Davis C. L. (1999). Enhancing microbiological safety of fresh orange juice by fruit immersion in hot water and chemical sanitizers. J. Food Prot. 62 756–760. 10.4315/0362-028x-62.7.756 10419268 Pao S. Kelsey D. F. Khalid M. F. Ettinger M. R. (2007). Using aqueous chlorine dioxide to prevent contamination of tomatoes with Salmonella enterica and Erwinia carotovora during fruit washing. J. Food Prot. 70 629–634. 10.4315/0362-028x-70.3.629 17388051 Park S. H. Kang D. H. (2015a). Antimicrobial effect of chlorine dioxide gas against foodborne pathogens under differing conditions of relative humidity. LWT Food Sci. Technol. 60 186–191. 10.1016/j.lwt.2014.09.031 Park S. H. Kang D. H. (2015b). Combination treatment of chlorine dioxide gas and aerosolized sanitizer for inactivating foodborne pathogens on spinach leaves and tomatoes. Int. J. Food Microbiol. 207 103–108. 10.1016/j.ijfoodmicro.2015.04.044 26001524 Park S. H. Kang D. H. (2018). Effect of temperature on chlorine dioxide inactivation of Escherichia coli O157:H7, Salmonella typhimurium, and Listeria monocytogenes on spinach, tomatoes, stainless steel, and glass surfaces. Int. J. Food Microbiol. 275 39–45. 10.1016/j.ijfoodmicro.2018.03.015 29627661 Popa I. Hanson E. J. Todd E. C. Schilder A. C. Ryser E. T. (2007). Efficacy of chlorine dioxide gas sachets for enhancing the microbiological quality and safety of blueberries. J. Food Prot. 70 2084–2088. 10.4315/0362-028x-70.9.2084 17900086 Praeger U. Herppich W. B. Hassenberg K. (2018). Aqueous chlorine dioxide treatment of horticultural produce: Effects on microbial safety and produce quality-A review. Crit. Rev. Food Sci. Nutr. 58 318–333. 10.1080/10408398.2016.1169157 27196114 Ray S. Jin T. Fan X. Liu L. Yam K. L. (2013). Development of chlorine dioxide releasing film and its application in decontaminating fresh produce. J. Food Sci. 78 M276–M284. 10.1111/1750-3841.12010 23294122 Rodgers S. L. Cash J. N. Siddiq M. Ryser E. T. (2004). A comparison of different chemical sanitizers for inactivating Escherichia coli O157:H7 and Listeria monocytogenes in solution and on apples, lettuce, strawberries, and cantaloupe. J. Food Prot. 67 721–731. 10.4315/0362-028x-67.4.721 15083724 Sharma V. K. Sohn M. (2012). Reactivity of chlorine dioxide with amino acids, peptides, and proteins. Environ. Chem. Lett. 10 255–264. 10.1007/s10311-012-0355-5 Simonet J. Gantzer C. (2006). Degradation of the Poliovirus 1 genome by chlorine dioxide. J. Appl. Microbiol. 100 862–870. 10.1111/j.1365-2672.2005.02850.x 16553743 Singh N. Singh R. K. Bhunia A. K. Stroshine R. L. (2002). Effect of inoculation and washing methods on the efficacy of different sanitizers against Escherichia coli O157:H7 on lettuce. Food Microbiol. 19 183–193. 10.1006/fmic.2001.0471 Singh S. Maji P. K. Lee Y. S. Gaikwad K. K. (2021). Applications of gaseous chlorine dioxide for antimicrobial food packaging: a review. Environ. Chem. Lett. 19 253–270. 10.1007/s10311-020-01085-8 Song H.-J. Choi D.-W. Song K. B. (2011). Effect of aqueous chlorine dioxide and UV-C treatment on the microbial reduction and color of cherry tomatoes. Horticult. Environ. Biotechnol. 52 488–493. 10.1007/s13580-011-0043-6 Sun X. Bai J. Ference C. Wang Z. Zhang Y. Narciso J. (2014). Antimicrobial activity of controlled-release chlorine dioxide gas on fresh blueberries. J. Food Prot. 77 1127–1132. 10.4315/0362-028X.JFP-13-554 24988018 Sun X. Baldwin E. Bai J. (2019). Applications of gaseous chlorine dioxide on postharvest handling and storage of fruits and vegetables – A review. Food Control 95 18–26. 10.1016/j.foodcont.2018.07.044 Sun X. Baldwin E. Plotto A. Narciso J. Ference C. Ritenour M. (2017b). Controlled-release of Chlorine Dioxide in a Perforated Packaging System to Extend the Storage Life and Improve the Safety of Grape Tomatoes. J. Vis. Exp. 2017:55400. 10.3791/55400 28448049 Sun X. Baldwin E. Ference C. Narciso J. Plotto A. Ritenour M. (2017a). The Effect of Controlled-release Chlorine Dioxide on the Preservation of Grapefruit. HortScience 52 122–126. 10.21273/hortsci11363-16 Sun X. Bin Z. Yaguang L. Christopher F. Elizabeth B. Ken H. (2017c). Effect of controlled-release chlorine dioxide on the quality and safety of cherry/grape tomatoes. Food Control 82, 26–30. 10.1016/j.foodcont.2017.06.021 Sy K. V. McWatters K. H. Beuchat L. R. (2005a). Efficacy of gaseous chlorine dioxide as a sanitizer for killing Salmonella, yeasts, and molds on blueberries, strawberries, and raspberries. J. Food Prot. 68 1165–1175. 10.4315/0362-028x-68.6.1165 15954703 Sy K. V. Murray M. B. Harrison M. D. Beuchat L. R. (2005b). Evaluation of gaseous chlorine dioxide as a sanitizer for killing Salmonella, Escherichia coli O157:H7, Listeria monocytogenes, and yeasts and molds on fresh and fresh-cut produce. J. Food Prot. 68 1176–1187. 10.4315/0362-028x-68.6.1176 15954704 Trinetta V. Linton R. H. Morgan M. T. (2013). Use of chlorine dioxide gas for the postharvest control of Alternaria alternata and Stemphylium vesicarium on Roma tomatoes. J. Sci. Food Agric. 93 3330–3333. 10.1002/jsfa.6180 23596000 Trinetta V. Morgan M. T. Linton R. H. (2010). Use of high-concentration-short-time chlorine dioxide gas treatments for the inactivation of Salmonella enterica spp. inoculated onto Roma tomatoes. Food Microbiol. 27 1009–1015. 10.1016/j.fm.2010.06.009 20832678 Trinetta V. Vaidya N. Linton R. Morgan M. (2011). Evaluation of chlorine dioxide gas residues on selected food produce. J. Food Sci. 76 T11–T15. 10.1111/j.1750-3841.2010.01911.x 21535724 Wang Z. Narciso J. Biotteau A. Plotto A. Baldwin E. Bai J. (2014). Improving Storability of Fresh Strawberries with Controlled Release Chlorine Dioxide in Perforated Clamshell Packaging. Food Bioproc. Technol. 7 3516–3524. 10.1007/s11947-014-1364-0 WHO (2015). WHO estimates of the global burden of foodborne diseases: foodborne disease burden epidemiology reference group 2007-2015. Geneva: WHO. Wu V. C. Kim B. (2007). Effect of a simple chlorine dioxide method for controlling five foodborne pathogens, yeasts and molds on blueberries. Food Microbiol. 24 794–800. 10.1016/j.fm.2007.03.010 17613378 Wu V. C. Rioux A. (2010). A simple instrument-free gaseous chlorine dioxide method for microbial decontamination of potatoes during storage. Food Microbiol. 27 179–184. 10.1016/j.fm.2009.08.007 19913711 Xue B. Jin M. Yang D. Guo X. Chen Z. Shen Z. (2013). Effects of chlorine and chlorine dioxide on human rotavirus infectivity and genome stability. Water Res. 47 3329–3338. 10.1016/j.watres.2013.03.025 23591108 Yoon J. H. Lee S. Y. (2018). Review: Comparison of the Effectiveness of Decontaminating Strategies for Fresh Fruits and Vegetables and Related Limitations. Crit. Rev. Food Sci. Nutr. 58 3189–3208. 10.1080/10408398.2017.1354813 28799790 Young S. B. Setlow P. (2003). Mechanisms of killing of Bacillus subtilis spores by hypochlorite and chlorine dioxide. J. Appl. Microbiol. 95 54–67. 10.1046/j.1365-2672.2003.01960.x 12807454 Zhang B. Huang C. Zhang L. Wang J. Huang X. Zhao Y. (2019). Application of chlorine dioxide microcapsule sustained-release antibacterial films for preservation of mangos. J. Food Sci. Technol. 56 1095–1103. 10.1007/s13197-019-03636-6 30956289 Zhang X. M. Fu M. R. (2018). Inhibitory effect of chlorine dioxide (ClO2) fumigation on growth and patulin production and its mechanism in Penicillum expansum. LWT 96 335–343. 10.1016/j.lwt.2018.05.051 Zhou S. Hu C. Zhao G. Jin T. Sheen S. Han L. (2018). Novel generation systems of gaseous chlorine dioxide for Salmonella inactivation on fresh tomato. Food Control 92 479–487. 10.1016/j.foodcont.2018.05.025 Zhu C. Chen Z. Yu G. (2013). Fungicidal mechanism of chlorine dioxide on Saccharomyces cerevisiae. Ann. Microbiol. 63 495–502. 10.1007/s13213-012-0494-8 Zhu Z. Guo Y. Yu P. Wang X. Zhang X. Dong W. (2019). Chlorine dioxide inhibits the replication of porcine reproductive and respiratory syndrome virus by blocking viral attachment. Infect. Genet. Evol. 67 78–87. 10.1016/j.meegid.2018.11.002 30395996 Abbreviations MAP

modified atmosphere packaging

 PPO

polyphenol oxidase

 PPM

parts per million.