Chlorine Dioxide: Friend or Foe for Cell Biomolecules? A Chemical Approach

This review examines the role of chlorine dioxide (ClO2) on inorganic compounds and cell biomolecules. As a disinfectant also present in drinking water, ClO2 helps to destroy bacteria, viruses, and some parasites. The Environmental Protection Agency EPA regulates the maximum concentration of chlorine dioxide in drinking water to be no more than 0.8 ppm. In any case, human consumption must be strictly regulated since, given its highly reactive nature, it can react with and oxidize many of the inorganic compounds found in natural waters. Simultaneously, chlorine dioxide reacts with natural organic matter in water, including humic and fulvic acids, forming oxidized organic compounds such as aldehydes and carboxylic acids, and rapidly oxidizes phenolic compounds, amines, amino acids, peptides, and proteins, as well as the nicotinamide adenine dinucleotide NADH, responsible for electron and proton exchange and energy production in all cells. The influence of ClO2 on biomolecules is derived from its interference with redox processes, modifying the electrochemical balances in mitochondrial and cell membranes. This discourages its use on an individual basis and without specialized monitoring by health professionals.


Introduction
Regarding chlorine dioxide (ClO 2 ), most of the reviews in the technical literature have been carried out from a biological or medical point of view, and others have analyzed its efficacy and safety as a disinfectant or in drinking water treatment. In this review, we focus on the chemical study of the interaction of ClO 2 with organic molecules or inorganic cations present in cells, giving an overview of its reactivity, its potential toxicity for biological molecules and hazardousness if not used correctly, and cases for which it has been approved.
Chlorine dioxide was discovered in 1811 by Sir Humphry Davy and since the mid-20th century, it has been widely used in the paper industry as a bleach and for the treatment of drinking water. More recent developments extend its application to food processing, disinfection of premises and vehicles, mold eradication, air disinfection and odor control, swimming pool treatment, wound cleaning, and dental applications [1].
Chlorine dioxide (ClO 2 ) is classified by the World Health Organization (WHO) as a safe and effective fourth generation, broad-spectrum, class A1 disinfectant [2,3]. It is used to purify drinking water without creating harmful concentrations of disinfection by-products [4]. The properties of ClO 2 result from one-electron transfer reactions, so it is considered a strong oxidizing agent [5] and, unlike chlorine, does not tend to react materials to form chlorinated species or with ammonia to form chloramine. Chlorin oxide is an important biocide and bleach and is used as an alternative to chlorine i purification and disinfection of drinking water [6]. ClO2 is used in 8.1% of drinking w treatment plants in the USA and 32.8% of those in China [7,8], and in some European c tries [9], it is used in paper bleaching, sterilization of medical devices, and disinfecti foodstuffs [10]. According to the EPA, ClO2 is used "in public water-treatment faciliti make water safe for drinking." When chlorine dioxide is added to drinking water, it to destroy bacteria, viruses, and some types of parasites that can make people sick, as Cryptosporidium parvum and Giardia lamblia.
Its main advantage over chlorine is that it reduces the formation of harmful org chlorine compounds [11][12][13][14][15][16][17]. ClO2 is beneficial in minimizing the formation of trihal thanes; however, ClO2 is converted to ClO2 − and ClO3 − , which can cause hemolytic an and other health effects. The Environmental Protection Agency (EPA) has set the m mum concentration in drinking water at 0.8 milligrams per liter (mg/L) for chlorine ide and 1.0 mg/L for chlorite ions [18]. Some of its industrial applications are listed in ure 1. Chlorine dioxide is a compound that differs from elemental chlorine, both chemical structure and in its behavior [19]. An important characteristic is its high solu in water, especially in cold water. Chlorine dioxide is about 10 times more soluble in w than chlorine.

Physicochemical Properties of ClO2
ClO2 is a yellowish-green gas and has a pungent odor, like Cl2, with a boiling of 11 °C, a melting point of −59 °C, a density of 1.64 g mL −1 (liquid) at 0 °C, a water bility of 3 g L −1 at 25 °C, and a pKa = 3. ClO2 is very soluble in water and does not h lyze, remaining in solution as a dissolved gas [20]. Solutions of ClO2 in water are s when protected from light and kept at room temperature or below, well-sealed Chlorine dioxide is a compound that differs from elemental chlorine, both in its chemical structure and in its behavior [19]. An important characteristic is its high solubility in water, especially in cold water. Chlorine dioxide is about 10 times more soluble in water than chlorine.

Physicochemical Properties of ClO 2
ClO 2 is a yellowish-green gas and has a pungent odor, like Cl 2 , with a boiling point of 11 • C, a melting point of −59 • C, a density of 1.64 g mL −1 (liquid) at 0 • C, a water solubility of 3 g L −1 at 25 • C, and a pKa = 3. ClO 2 is very soluble in water and does not hydrolyze, remaining in solution as a dissolved gas [20]. Solutions of ClO 2 in water are stable when protected from light and kept at room temperature or below, well-sealed, and slightly acidified (pH = 6). The ultraviolet absorption spectrum of ClO 2 solutions is broadband with a peak at 359 nm and a molar extinction coefficient of 1250 M −1 cm −1 . ClO 2 has a relatively short half-life and is highly volatile and explosive at concentrations > 10% in air [21]. Chlorine dioxide may not be compressed, stored, or transported under pressure and must be manufactured at the place of consumption.
ClO 2 is a neutral monomeric free radical with a dipole moment of 1.792 Debye [22]. From the microwave spectra of gas-phase chlorine dioxide, the chlorine-oxygen distance is found to be approximately 0.147 nm and electron diffraction indicates 0.149 nm. This chlorine-oxygen distance is approximately that of an average chlorine-oxygen double bond. Studies on the geometry of ClO 2 established that the bond distance between the Cl atom and the O atom is smaller compared to the bond in chlorine monoxide (ClO). These results explain and justify the representation of the double bond between these two atoms, as well as showing that resonance structures satisfactorily explain the unpaired electron of the chlorine atom. ClO 2 has a molecular geometry with an oxygen-chlorine-oxygen bond angle of 117.6 • , as shown in Figure 2. In its ground state, although the unpaired electron is shared between the two oxygen atoms and the chlorine atom, most of the electron density resides mainly on either oxygen atom.
bond. Studies on the geometry of ClO2 established that the bond distance between th atom and the O atom is smaller compared to the bond in chlorine monoxide (ClO). Th results explain and justify the representation of the double bond between these two ato as well as showing that resonance structures satisfactorily explain the unpaired elect of the chlorine atom. ClO2 has a molecular geometry with an oxygen-chlorine-oxy bond angle of 117.6°, as shown in Figure 2. In its ground state, although the unpai electron is shared between the two oxygen atoms and the chlorine atom, most of the e tron density resides mainly on either oxygen atom.
It has an odd number of valence electrons (it is a paramagnetic radical), and its e tronic structure has long puzzled chemists, because none of the possible Lewis structu are satisfactory. In 1933, Brockway proposed a structure involving a three-elect bond [23]; Linus Pauling later developed this idea and proposed two possible reson structures involving a double bond on the one hand and a single bond with a three-e tron bond on the other [24].
The electronegativity of the two oxygen atoms is large enough to eliminate the e tron density of the chlorine atom and gives chlorine a partial positive charge, Figure 2

Generation of Chlorine Dioxide
Chlorine dioxide is a widely used disinfectant as an alternative to chlorine, due to effectiveness in pathogen inactivation and low production of halogenated organic products of disinfection. However, during the generation of ClO2, chlorine is inevita introduced into the ClO2 solution obtained as an impurity. The presence of chlorin chlorine dioxide may affect the formation and toxicity of disinfection by-products as w as the disinfection efficiency.
There are different methods for the preparation of chlorine dioxide [16], depend on the amount required, the number of by-products that can be tolerated, and whet the gas is required in solution or in gaseous form, Figure 3. It has an odd number of valence electrons (it is a paramagnetic radical), and its electronic structure has long puzzled chemists, because none of the possible Lewis structures are satisfactory. In 1933, Brockway proposed a structure involving a three-electron bond [23]; Linus Pauling later developed this idea and proposed two possible resonant structures involving a double bond on the one hand and a single bond with a three-electron bond on the other [24].
The electronegativity of the two oxygen atoms is large enough to eliminate the electron density of the chlorine atom and gives chlorine a partial positive charge, Figure 2.

Generation of Chlorine Dioxide
Chlorine dioxide is a widely used disinfectant as an alternative to chlorine, due to its effectiveness in pathogen inactivation and low production of halogenated organic byproducts of disinfection. However, during the generation of ClO 2 , chlorine is inevitably introduced into the ClO 2 solution obtained as an impurity. The presence of chlorine in chlorine dioxide may affect the formation and toxicity of disinfection by-products as well as the disinfection efficiency.
There are different methods for the preparation of chlorine dioxide [16], depending on the amount required, the number of by-products that can be tolerated, and whether the gas is required in solution or in gaseous form, Figure 3.

From Chlorite Ions
ClO2 is generated from chlorite ions using chemicals, electrochemicals, and biocatalysts, and from the reaction of chlorite with chlorine gas Cl2 or hydrochloric acid (HCl) [25][26][27], as shown in Figure 4. The methods described in Figure 4 have major disadvantages due to the production of high amounts of chlorides, which can be avoided by replacing hydrochloric with sulfuric acid, although in such cases, the processes become less efficient. These methods involve concentrated acids and/or externally added oxidants such as Cl2, OCl − , and H2O2.
Another way to generate ClO2 from chlorite by one-electron transfer is by electrochemical means [28], but this procedure requires a considerable input of electrical energy. An electrochemical method using mixed metal oxide MMO electrodes in the presence of chlorite and boron-doped diamond BDD anodes to promote the evolution of chlorine species was also studied [29,30]. Another possibility is to start from an undoped solution of sodium chlorite and a mixture of sodium chloride in an undivided electrochemical cell with a constant current, Ti/IrO2 anode, and Ti/Pt cathode [31,32].
To oxidize chlorite to ClO2, catalysts are based on manganese or iron porphyrin complexes. In these systems, chlorite dismutation is initiated through the oxidation of Mn(II or III) or Fe(III) by chlorite ions to produce hypochlorite ions and high-valent Mn and Fe(IV or V). Both oxidation states, IV and V, oxidize chlorite directly to ClO2, although complete conversion of chlorite to ClO2 was achieved in water using water-soluble Fe or Mn porphyrins. The synthesis of these ligands and catalysts is very expensive. A catalytic process has also been developed using a manganese porphyrin catalyst, tetra-kis-5,10,15,20-(N,N-dimethylimidazolium) porphyrinatomanganese(III), which is soluble in water and catalyzes the formation of chlorine dioxide from chlorite at room temperature and pH = 5 [33][34][35][36].

From Sodium Chlorate
Currently, the most widely used method to produce chlorine dioxide is the reduction method, by reacting sodium chlorate in a concentrated acid solution with reducing agents

From Chlorite Ions
ClO 2 is generated from chlorite ions using chemicals, electrochemicals, and biocatalysts, and from the reaction of chlorite with chlorine gas Cl 2 or hydrochloric acid (HCl) [25][26][27], as shown in Figure 4.

From Chlorite Ions
ClO2 is generated from chlorite ions using chemicals, electrochemicals, and biocatalysts, and from the reaction of chlorite with chlorine gas Cl2 or hydrochloric acid (HCl) [25][26][27], as shown in Figure 4. The methods described in Figure 4 have major disadvantages due to the production of high amounts of chlorides, which can be avoided by replacing hydrochloric with sulfuric acid, although in such cases, the processes become less efficient. These methods involve concentrated acids and/or externally added oxidants such as Cl2, OCl − , and H2O2.
Another way to generate ClO2 from chlorite by one-electron transfer is by electrochemical means [28], but this procedure requires a considerable input of electrical energy. An electrochemical method using mixed metal oxide MMO electrodes in the presence of chlorite and boron-doped diamond BDD anodes to promote the evolution of chlorine species was also studied [29,30]. Another possibility is to start from an undoped solution of sodium chlorite and a mixture of sodium chloride in an undivided electrochemical cell with a constant current, Ti/IrO2 anode, and Ti/Pt cathode [31,32].
To oxidize chlorite to ClO2, catalysts are based on manganese or iron porphyrin complexes. In these systems, chlorite dismutation is initiated through the oxidation of Mn(II or III) or Fe(III) by chlorite ions to produce hypochlorite ions and high-valent Mn and Fe(IV or V). Both oxidation states, IV and V, oxidize chlorite directly to ClO2, although complete conversion of chlorite to ClO2 was achieved in water using water-soluble Fe or Mn porphyrins. The synthesis of these ligands and catalysts is very expensive. A catalytic process has also been developed using a manganese porphyrin catalyst, tetra-kis-5,10,15,20-(N,N-dimethylimidazolium) porphyrinatomanganese(III), which is soluble in water and catalyzes the formation of chlorine dioxide from chlorite at room temperature and pH = 5 [33][34][35][36].

From Sodium Chlorate
Currently, the most widely used method to produce chlorine dioxide is the reduction method, by reacting sodium chlorate in a concentrated acid solution with reducing agents The methods described in Figure 4 have major disadvantages due to the production of high amounts of chlorides, which can be avoided by replacing hydrochloric with sulfuric acid, although in such cases, the processes become less efficient. These methods involve concentrated acids and/or externally added oxidants such as Cl 2 , OCl − , and H 2 O 2 .
Another way to generate ClO 2 from chlorite by one-electron transfer is by electrochemical means [28], but this procedure requires a considerable input of electrical energy. An electrochemical method using mixed metal oxide MMO electrodes in the presence of chlorite and boron-doped diamond BDD anodes to promote the evolution of chlorine species was also studied [29,30]. Another possibility is to start from an undoped solution of sodium chlorite and a mixture of sodium chloride in an undivided electrochemical cell with a constant current, Ti/IrO2 anode, and Ti/Pt cathode [31,32].
To oxidize chlorite to ClO 2 , catalysts are based on manganese or iron porphyrin complexes. In these systems, chlorite dismutation is initiated through the oxidation of Mn(II or III) or Fe(III) by chlorite ions to produce hypochlorite ions and high-valent Mn and Fe(IV or V). Both oxidation states, IV and V, oxidize chlorite directly to ClO 2 , although complete conversion of chlorite to ClO 2 was achieved in water using water-soluble Fe or Mn porphyrins. The synthesis of these ligands and catalysts is very expensive. A catalytic process has also been developed using a manganese porphyrin catalyst, tetra-kis-5,10,15,20-(N,N-dimethylimidazolium) porphyrinatomanganese(III), which is soluble in water and catalyzes the formation of chlorine dioxide from chlorite at room temperature and pH = 5 [33][34][35][36].

From Sodium Chlorate
Currently, the most widely used method to produce chlorine dioxide is the reduction method, by reacting sodium chlorate in a concentrated acid solution with reducing agents such as sulfur dioxide, methanol, oxalic acid, hydrogen peroxide, hydrochloric acid, or sodium chloride. With hydrochloric acid, the chlorine content is high, the purity of the chlorine dioxide is low, and the contamination is severe [37,38].
The sulfur dioxide method has the disadvantage of SO 2 [38], with side reactions and low efficiency, which limits its application. The methanol process is currently the most widely used method for chlorine dioxide production in new-build plants worldwide [37]. The chlorine dioxide obtained is of high purity, but this method requires high acidity, and the reactor needs materials with excellent corrosion resistance.
In the chlorate reduction method, hydrogen peroxide advantageously replaces the other reagents, the process is more environmentally friendly, and the main by-product formed is oxygen, Figure 5. such as sulfur dioxide, methanol, oxalic acid, hydrogen peroxide, hydrochloric acid, or sodium chloride. With hydrochloric acid, the chlorine content is high, the purity of the chlorine dioxide is low, and the contamination is severe [37,38]. The sulfur dioxide method has the disadvantage of SO2 [38], with side reactions and low efficiency, which limits its application. The methanol process is currently the most widely used method for chlorine dioxide production in new-build plants worldwide [37]. The chlorine dioxide obtained is of high purity, but this method requires high acidity, and the reactor needs materials with excellent corrosion resistance.
In the chlorate reduction method, hydrogen peroxide advantageously replaces the other reagents, the process is more environmentally friendly, and the main by-product formed is oxygen, Figure 5. The reaction between commercial solutions of chlorate and H2O2 results in the formation of ClO2 [38]. The reaction is very reproducible and stoichiometric. It is very important that the reaction mixture is not depleted of chlorate to avoid further reduction of ClO2. Once ClO2 is formed, the reduction of the chlorinated species continues, leading to the formation of other species, such as chlorite, Figure 6. When large quantities of chlorine dioxide are needed, sodium chlorate is used as a raw material, and this method has traditionally been used in the pulp and paper industries. The conditions for producing ClO2 from sodium chlorite can be better controlled than those for sodium chlorate, but chlorite is more expensive and unstable, and therefore, from an industrial point of view, sodium chlorate is a more suitable feedstock [39]. The reaction between commercial solutions of chlorate and H 2 O 2 results in the formation of ClO 2 [38]. The reaction is very reproducible and stoichiometric. It is very important that the reaction mixture is not depleted of chlorate to avoid further reduction of ClO 2 . Once ClO 2 is formed, the reduction of the chlorinated species continues, leading to the formation of other species, such as chlorite, Figure 6. such as sulfur dioxide, methanol, oxalic acid, hydrogen peroxide, hydrochloric acid, or sodium chloride. With hydrochloric acid, the chlorine content is high, the purity of the chlorine dioxide is low, and the contamination is severe [37,38]. The sulfur dioxide method has the disadvantage of SO2 [38], with side reactions and low efficiency, which limits its application. The methanol process is currently the most widely used method for chlorine dioxide production in new-build plants worldwide [37]. The chlorine dioxide obtained is of high purity, but this method requires high acidity, and the reactor needs materials with excellent corrosion resistance.
In the chlorate reduction method, hydrogen peroxide advantageously replaces the other reagents, the process is more environmentally friendly, and the main by-product formed is oxygen, Figure 5. The reaction between commercial solutions of chlorate and H2O2 results in the formation of ClO2 [38]. The reaction is very reproducible and stoichiometric. It is very important that the reaction mixture is not depleted of chlorate to avoid further reduction of ClO2. Once ClO2 is formed, the reduction of the chlorinated species continues, leading to the formation of other species, such as chlorite, Figure 6. When large quantities of chlorine dioxide are needed, sodium chlorate is used as a raw material, and this method has traditionally been used in the pulp and paper industries. The conditions for producing ClO2 from sodium chlorite can be better controlled than those for sodium chlorate, but chlorite is more expensive and unstable, and therefore, from an industrial point of view, sodium chlorate is a more suitable feedstock [39]. When large quantities of chlorine dioxide are needed, sodium chlorate is used as a raw material, and this method has traditionally been used in the pulp and paper industries. The conditions for producing ClO 2 from sodium chlorite can be better controlled than those for sodium chlorate, but chlorite is more expensive and unstable, and therefore, from an industrial point of view, sodium chlorate is a more suitable feedstock [39].

Disproportionation of Chlorine Dioxide with OH −
In solution at neutral pH, in the absence of light, and at room temperature or below, chlorine dioxide is fairly stable [40], but its decomposition is accelerated in alkaline solution to give

Disproportionation of Chlorine Dioxide with OH −
In solution at neutral pH, in the absence of light, and at room temperature or below, chlorine dioxide is fairly stable [40], but its decomposition is accelerated in alkaline solution to give ClO2 − and ClO3 − [41], Figure 7. Ion chromatography shows that ClO2 − and ClO3 − are the only chlorine products formed from the decomposition of ClO2 in a basic solution. However, the ratio of ClO2 − to ClO3 − is not 1:1 as required for the disproportionation reaction. According to several authors, the percentage of ClO2 − is higher than that of ClO3 − as the ClO2 concentration decreases. At micromolar levels of ClO2 the yield of ClO2 − is higher than that of ClO3 − . The following additional reaction could explain the change of molar stoichiometry from ClO2 − to ClO3 − [42], Figure 8. The three possible mechanisms (Figures 9-11) can explain the stoichiometry of the decomposition of ClO2 in alkaline solution, via assisted electron transfer [41].
In the mechanism of ClO3 − formation from ClO2 in basic media, the reaction of ClO2 with OH − generates species where OH − binds to the Cl atom of ClO2 to form the intermediate (HOCl(O)O) − . The formation of ClO3 − occurred from the reaction between HOClO2 and OH − . This pathway shows first order kinetics with respect to the concentrations of ClO2 and OH − , Figure 9. For the formation of ClO2 − in basic media, it is proposed that OH-forms an adduct with one of the oxygen atoms of ClO2 to give OClOOH − , and OCl is weakly bound to OOH. This adduct can undergo rapid electron transfer with a second ClO2 to give ClO2 − and OClOOH. The latter species reacts favorably with OH − to generate HOClO and HOO − . The reaction between HOO − and ClO2 gives ClO2 − and O2 [43], Figure 10.

Disproportionation of Chlorine Dioxide with OH −
In solution at neutral pH, in the absence of light, and at room temperature or below, chlorine dioxide is fairly stable [40], but its decomposition is accelerated in alkaline solution to give ClO2 − and ClO3 − [41], Figure 7. Ion chromatography shows that ClO2 − and ClO3 − are the only chlorine products formed from the decomposition of ClO2 in a basic solution. However, the ratio of ClO2 − to ClO3 − is not 1:1 as required for the disproportionation reaction. According to several authors, the percentage of ClO2 − is higher than that of ClO3 − as the ClO2 concentration decreases. At micromolar levels of ClO2 the yield of ClO2 − is higher than that of ClO3 − . The following additional reaction could explain the change of molar stoichiometry from ClO2 − to ClO3 − [42], Figure 8. The three possible mechanisms (Figures 9-11) can explain the stoichiometry of the decomposition of ClO2 in alkaline solution, via assisted electron transfer [41].
In the mechanism of ClO3 − formation from ClO2 in basic media, the reaction of ClO2 with OH − generates species where OH − binds to the Cl atom of ClO2 to form the intermediate (HOCl(O)O) − . The formation of ClO3 − occurred from the reaction between HOClO2 and OH − . This pathway shows first order kinetics with respect to the concentrations of ClO2 and OH − , Figure 9. For the formation of ClO2 − in basic media, it is proposed that OH-forms an adduct with one of the oxygen atoms of ClO2 to give OClOOH − , and OCl is weakly bound to OOH. This adduct can undergo rapid electron transfer with a second ClO2 to give ClO2 − and OClOOH. The latter species reacts favorably with OH − to generate HOClO and HOO − . The reaction between HOO − and ClO2 gives ClO2 − and O2 [43], Figure 10. The three possible mechanisms (Figures 9-11) can explain the stoichiometry of the decomposition of ClO 2 in alkaline solution, via assisted electron transfer [41]. chlorine dioxide is fairly stable [40], but its decomposition is accelerated in alkaline solution to give ClO2 − and ClO3 − [41], Figure 7. Ion chromatography shows that ClO2 − and ClO3 − are the only chlorine products formed from the decomposition of ClO2 in a basic solution. However, the ratio of ClO2 − to ClO3 − is not 1:1 as required for the disproportionation reaction. According to several authors, the percentage of ClO2 − is higher than that of ClO3 − as the ClO2 concentration decreases. At micromolar levels of ClO2 the yield of ClO2 − is higher than that of ClO3 − . The following additional reaction could explain the change of molar stoichiometry from ClO2 − to ClO3 − [42], Figure 8.  [41].
In the mechanism of ClO3 − formation from ClO2 in basic media, the reaction of ClO2 with OH − generates species where OH − binds to the Cl atom of ClO2 to form the intermediate (HOCl(O)O) − . The formation of ClO3 − occurred from the reaction between HOClO2 and OH − . This pathway shows first order kinetics with respect to the concentrations of ClO2 and OH − , Figure 9. For the formation of ClO2 − in basic media, it is proposed that OH-forms an adduct with one of the oxygen atoms of ClO2 to give OClOOH − , and OCl is weakly bound to OOH. This adduct can undergo rapid electron transfer with a second ClO2 to give ClO2 − and OClOOH. The latter species reacts favorably with OH − to generate HOClO and HOO − . The reaction between HOO − and ClO2 gives ClO2 − and O2 [43], Figure 10. A third possibility involves the formation of an intermediate dimer [44], Cl2O4, which reacts with OH − (an electron transfer step). This pathway is important at high ClO2 concentrations, Figure 11.  A third possibility involves the formation of an intermediate dimer [44], Cl2O4, which reacts with OH − (an electron transfer step). This pathway is important at high ClO2 concentrations, Figure 11. The distribution of chlorine dioxide decomposition products in a basic solution changes as the ClO2 concentration decreases. While disproportionation reactions giving equal amounts of ClO2 − and ClO3 − dominate the stoichiometry at millimolar or higher ClO2 levels, the ratio of ClO2 − to ClO3 − formed increases significantly at micromolar levels of ClO2 [42].
The kinetic evidence shows three concurrent pathways that show a first order dependence on [OH − ] but have a variable order on [ClO2]. Pathway 1 is a disproportionation reaction that is first order in [ClO2], Figure 12. Pathway 2, a previously unknown reaction, is also first order in [ClO2] but forms ClO2 − as the only chlorine-containing product. Pathway 2 is attributed to the attack of OH − on an oxygen atom of ClO2 leading to intermediate peroxide intermediates and producing ClO2 − and O2 as products. This pathway is important at low levels of ClO2, Figure 13.  In the mechanism of ClO 3 − formation from ClO 2 in basic media, the reaction of ClO 2 with OH − generates species where OH − binds to the Cl atom of ClO 2 to form the intermediate (HOCl(O)O) − . The formation of ClO 3 − occurred from the reaction between HOClO 2 and OH − . This pathway shows first order kinetics with respect to the concentrations of ClO 2 and OH − , Figure 9.
For the formation of ClO 2 − in basic media, it is proposed that OH-forms an adduct with one of the oxygen atoms of ClO 2 to give OClOOH − , and OCl is weakly bound to OOH. This adduct can undergo rapid electron transfer with a second ClO 2 to give ClO 2 − and OClOOH. The latter species reacts favorably with OH − to generate HOClO and HOO − . The reaction between HOO − and ClO 2 gives ClO 2 − and O 2 [43], Figure 10. A third possibility involves the formation of an intermediate dimer [44], Cl 2 O 4 , which reacts with OH − (an electron transfer step). This pathway is important at high ClO 2 concentrations, Figure 11.
The distribution of chlorine dioxide decomposition products in a basic solution changes as the ClO 2 concentration decreases. While disproportionation reactions giving equal amounts of ClO 2 − and ClO 3 − dominate the stoichiometry at millimolar or higher ClO 2 levels, the ratio of ClO 2 − to ClO 3 − formed increases significantly at micromolar levels of ClO 2 [42].
The kinetic evidence shows three concurrent pathways that show a first order dependence on [OH − ] but have a variable order on [ClO 2 ]. Pathway 1 is a disproportionation reaction that is first order in [ClO 2 ], Figure 12. A third possibility involves the formation of an intermediate dimer [44], Cl2O4, which reacts with OH − (an electron transfer step). This pathway is important at high ClO2 concentrations, Figure 11. The distribution of chlorine dioxide decomposition products in a basic solution changes as the ClO2 concentration decreases. While disproportionation reactions giving equal amounts of ClO2 − and ClO3 − dominate the stoichiometry at millimolar or higher ClO2 levels, the ratio of ClO2 − to ClO3 − formed increases significantly at micromolar levels of ClO2 [42].
The kinetic evidence shows three concurrent pathways that show a first order dependence on [OH − ] but have a variable order on [ClO2]. Pathway 1 is a disproportionation reaction that is first order in [ClO2], Figure 12. Pathway 2, a previously unknown reaction, is also first order in [ClO2] but forms ClO2 − as the only chlorine-containing product. Pathway 2 is attributed to the attack of OH − on an oxygen atom of ClO2 leading to intermediate peroxide intermediates and producing ClO2 − and O2 as products. This pathway is important at low levels of ClO2, Figure 13.   A third possibility involves the formation of an intermediate dimer [44], Cl2O4, which reacts with OH − (an electron transfer step). This pathway is important at high ClO2 concentrations, Figure 11. The distribution of chlorine dioxide decomposition products in a basic solution changes as the ClO2 concentration decreases. While disproportionation reactions giving equal amounts of ClO2 − and ClO3 − dominate the stoichiometry at millimolar or higher ClO2 levels, the ratio of ClO2 − to ClO3 − formed increases significantly at micromolar levels of ClO2 [42].
The kinetic evidence shows three concurrent pathways that show a first order dependence on [OH − ] but have a variable order on [ClO2]. Pathway 1 is a disproportionation reaction that is first order in [ClO2], Figure 12. Pathway 2, a previously unknown reaction, is also first order in [ClO2] but forms ClO2 − as the only chlorine-containing product. Pathway 2 is attributed to the attack of OH − on an oxygen atom of ClO2 leading to intermediate peroxide intermediates and producing ClO2 − and O2 as products. This pathway is important at low levels of ClO2, Figure 13.

Disproportionation of Chlorine Dioxide with Nucleophile
The effect of OX − hypohalite ion catalysis on the disproportionation of chlorine dioxide in basic solution to give ClO2 − and ClO3 − has been studied. In the first step of hypohalite catalysis (the reaction between ClO2 and OX − involved a transfer of electrons to form ClO2 − and OX), this step is reversible [45][46][47], Figure 15. In the second step, the reactions between ClO2 and XO form XOClO2, Figure 16. In basic medium, hydrolysis of XOClO2 produces ClO3 − and OX − , Figure 17.

Photodissociation of ClO2
The reactivity of ClO2 is modified by exposure to UV radiation in a process known as UV/ClO2. ClO2 undergoes photodissociation leading to the formation of the primary radical oxygen (O • ), chlorine (Cl • ), and chlorine oxide (ClO • ) by homolytic fission of the chlorine-oxygen bond to form ClO • and O • [48][49][50]. Illumination of a neutral aqueous ClO2 solution gives a mixture of chloric acid and hydrochloric acid, Figure 18.

Disproportionation of Chlorine Dioxide with Nucleophile
The effect of OX − hypohalite ion catalysis on the disproportionation of chlorine dioxide in basic solution to give ClO 2 − and ClO 3 − has been studied. In the first step of hypohalite catalysis (the reaction between ClO 2 and OX − involved a transfer of electrons to form ClO 2 − and OX), this step is reversible [45][46][47], Figure 15.

Disproportionation of Chlorine Dioxide with Nucleophile
The effect of OX − hypohalite ion catalysis on the disproportionation of chlorine dioxide in basic solution to give ClO2 − and ClO3 − has been studied. In the first step of hypohalite catalysis (the reaction between ClO2 and OX − involved a transfer of electrons to form ClO2 − and OX), this step is reversible [45][46][47], Figure 15. In the second step, the reactions between ClO2 and XO form XOClO2, Figure 16. In basic medium, hydrolysis of XOClO2 produces ClO3 − and OX − , Figure 17.

Photodissociation of ClO2
The reactivity of ClO2 is modified by exposure to UV radiation in a process known as UV/ClO2. ClO2 undergoes photodissociation leading to the formation of the primary radical oxygen (O • ), chlorine (Cl • ), and chlorine oxide (ClO • ) by homolytic fission of the chlorine-oxygen bond to form ClO • and O • [48][49][50]. Illumination of a neutral aqueous ClO2 solution gives a mixture of chloric acid and hydrochloric acid, Figure 18.  In the second step, the reactions between ClO 2 and XO form XOClO 2 , Figure 16.
Pathway 3 is second order in [ClO2] and generates equal amounts of ClO2 − and ClO3 − . A Cl2O4 intermediate is proposed for this pathway. At high ClO2 concentrations, pathway 3 brings the overall yield of ClO3 − close to the overall yield of ClO2 − , Figure 14.

Disproportionation of Chlorine Dioxide with Nucleophile
The effect of OX − hypohalite ion catalysis on the disproportionation of chlorine dioxide in basic solution to give ClO2 − and ClO3 − has been studied. In the first step of hypohalite catalysis (the reaction between ClO2 and OX − involved a transfer of electrons to form ClO2 − and OX), this step is reversible [45][46][47], Figure 15. In the second step, the reactions between ClO2 and XO form XOClO2, Figure 16. In basic medium, hydrolysis of XOClO2 produces ClO3 − and OX − , Figure 17.

Photodissociation of ClO2
The reactivity of ClO2 is modified by exposure to UV radiation in a process known as UV/ClO2. ClO2 undergoes photodissociation leading to the formation of the primary radical oxygen (O • ), chlorine (Cl • ), and chlorine oxide (ClO • ) by homolytic fission of the chlorine-oxygen bond to form ClO • and O • [48][49][50]. Illumination of a neutral aqueous ClO2 solution gives a mixture of chloric acid and hydrochloric acid, Figure 18.

Disproportionation of Chlorine Dioxide with Nucleophile
The effect of OX − hypohalite ion catalysis on the disproportionation of chlorine dioxide in basic solution to give ClO2 − and ClO3 − has been studied. In the first step of hypohalite catalysis (the reaction between ClO2 and OX − involved a transfer of electrons to form ClO2 − and OX), this step is reversible [45][46][47], Figure 15. In the second step, the reactions between ClO2 and XO form XOClO2, Figure 16. In basic medium, hydrolysis of XOClO2 produces ClO3 − and OX − , Figure 17.

Photodissociation of ClO2
The reactivity of ClO2 is modified by exposure to UV radiation in a process known as UV/ClO2. ClO2 undergoes photodissociation leading to the formation of the primary radical oxygen (O • ), chlorine (Cl • ), and chlorine oxide (ClO • ) by homolytic fission of the chlorine-oxygen bond to form ClO • and O • [48][49][50]. Illumination of a neutral aqueous ClO2 solution gives a mixture of chloric acid and hydrochloric acid, Figure 18.

Photodissociation of ClO 2
The reactivity of ClO 2 is modified by exposure to UV radiation in a process known as UV/ClO 2 . ClO 2 undergoes photodissociation leading to the formation of the primary radical oxygen (O • ), chlorine (Cl • ), and chlorine oxide (ClO • ) by homolytic fission of the chlorine-oxygen bond to form ClO • and O • [48][49][50]. Illumination of a neutral aqueous ClO 2 solution gives a mixture of chloric acid and hydrochloric acid, Figure 18.

Disproportionation of Chlorine Dioxide with Nucleophile
The effect of OX − hypohalite ion catalysis on the disproportionation of chlorine dioxide in basic solution to give ClO2 − and ClO3 − has been studied. In the first step of hypohalite catalysis (the reaction between ClO2 and OX − involved a transfer of electrons to form ClO2 − and OX), this step is reversible [45][46][47], Figure 15. In the second step, the reactions between ClO2 and XO form XOClO2, Figure 16. In basic medium, hydrolysis of XOClO2 produces ClO3 − and OX − , Figure 17.

Photodissociation of ClO2
The reactivity of ClO2 is modified by exposure to UV radiation in a process known as UV/ClO2. ClO2 undergoes photodissociation leading to the formation of the primary radical oxygen (O • ), chlorine (Cl • ), and chlorine oxide (ClO • ) by homolytic fission of the chlorine-oxygen bond to form ClO • and O • [48][49][50]. Illumination of a neutral aqueous ClO2 solution gives a mixture of chloric acid and hydrochloric acid, Figure 18.  The photochemical and thermal decomposition of ClO 2 takes place by homolytic fission of the chlorine-oxygen bond, Figure 19. The photochemical and thermal decomposition of ClO2 takes place by homolytic fission of the chlorine-oxygen bond, Figure 19. Once homolytic fission has occurred, further reactions will depend on the reaction conditions. At room temperature, photolysis of dry, gaseous ClO2 gives Cl2, O2, and some ClO3, which subsequently dimerizes to Cl2O6 or undergoes further photolysis to Cl2 and Once homolytic fission has occurred, further reactions will depend on the reaction conditions. At room temperature, photolysis of dry, gaseous ClO 2 gives Cl 2 , O 2 , and some ClO 3 , which subsequently dimerizes to Cl 2 O 6 or undergoes further photolysis to Cl 2 and O 2 , Figure 20.
The photochemical and thermal decomposition of ClO2 takes place by homolytic fission of the chlorine-oxygen bond, Figure 19. Once homolytic fission has occurred, further reactions will depend on the reaction conditions. At room temperature, photolysis of dry, gaseous ClO2 gives Cl2, O2, and some ClO3, which subsequently dimerizes to Cl2O6 or undergoes further photolysis to Cl2 and O2, Figure 20. The degradation mechanisms and radical chemistry associated with UVC photolysis of ClO2 are quite complicated [51]. The photolysis of ClO2 by UVC light provides ClO − and oxygen by cleavage of the Cl-O [52] and Cl • [53] bond, Figure 21. The above species can undergo chain reactions to generate secondary reactive species [54,55], Figure 22.  The degradation mechanisms and radical chemistry associated with UVC photolysis of ClO 2 are quite complicated [51]. The photolysis of ClO 2 by UVC light provides ClO − and oxygen by cleavage of the Cl-O [52] and Cl • [53] bond, Figure 21.
sion of the chlorine-oxygen bond, Figure 19. Once homolytic fission has occurred, further reactions will depend on the reaction conditions. At room temperature, photolysis of dry, gaseous ClO2 gives Cl2, O2, and some ClO3, which subsequently dimerizes to Cl2O6 or undergoes further photolysis to Cl2 and O2, Figure 20. The degradation mechanisms and radical chemistry associated with UVC photolysis of ClO2 are quite complicated [51]. The photolysis of ClO2 by UVC light provides ClO − and oxygen by cleavage of the Cl-O [52] and Cl • [53] bond, Figure 21. The above species can undergo chain reactions to generate secondary reactive species [54,55], Figure 22.  The above species can undergo chain reactions to generate secondary reactive species [54,55], Figure 22.
Once homolytic fission has occurred, further reactions will depend on the reacti conditions. At room temperature, photolysis of dry, gaseous ClO2 gives Cl2, O2, and som ClO3, which subsequently dimerizes to Cl2O6 or undergoes further photolysis to Cl2 a O2, Figure 20. The degradation mechanisms and radical chemistry associated with UVC photoly of ClO2 are quite complicated [51]. The photolysis of ClO2 by UVC light provides ClO − a oxygen by cleavage of the Cl-O [52] and Cl • [53] bond, Figure 21. The above species can undergo chain reactions to generate secondary reactive sp cies [54,55], Figure 22.  The degradation of ClO 2 under UVC radiation accelerates the tendency of chlorite and chlorate formation compared to ClO 2 alone. In addition, chlorite and chlorate can also be generated from radical-radical interactions [56][57][58][59], Figure 23. The degradation of ClO2 under UVC radiation accelerates the tendency of chlorite and chlorate formation compared to ClO2 alone. In addition, chlorite and chlorate can also be generated from radical-radical interactions [56][57][58][59], Figure 23.

Reactivity of ClO2
The chemistry of ClO2 is complex compared to that of other chlorine compounds, because of its high reactivity. Chlorine dioxide is a strong oxidizing agent and, unlike chlorine, does not tend to react with organic materials to form chlorinated species, or with ammonia to form chloramine. The oxidation of ClO2 generally begins with the removal of an electron from residual organic compounds to produce organic radicals and ClO2 − . Subsequent oxidation of the organic radicals by ClO2 involves oxygen transfer with the release of HOCl or electron transfer with the release of ClO2 − [46,50].
Inorganic compounds are important in the body and are responsible for many simple functions. The major inorganic compounds are H2O, molecular oxygen O2, carbon dioxide CO2, and some acids, bases, and salts. Iron is a biologically essential component of every living organism and various cellular mechanisms have evolved to capture iron from the environment in biologically useful forms [60]. It is primarily involved in the transfer of oxygen from the lungs to tissues. However, iron also plays a role in metabolism as a component of some proteins and enzymes. Manganese (Mn) is a trace mineral that is present in tiny amounts in the body. It is found mostly in bones, the liver, kidneys, and pancreas, and helps the body form connective tissue, bones, blood clotting factors, and sex hormones. Manganese is a cofactor for many enzymes, including manganese superoxide dismutase, arginase, and pyruvate carboxylase. In these enzymes, manganese is involved in the metabolism of amino acids, cholesterol, glucose, and carbohydrates; the elimination of reactive oxygen species; bone formation; reproduction; immune response; and blood coagulation and hemostasis together with vitamin K [61][62][63][64][65][66][67].
Some researchers have studied the reactivity of ClO2 with inorganic and organic compounds has been studied [68]. In the human body, ClO2 can react with I − , NO2 − , O3, H2O2, Fe(II), and Mn(II). The rate constants with tertiary amines and phenols were also high at pH ≥ 6. ClO2 does not react with ammonia, Br − , carbohydrates, aromatic hydro-carbides, and compounds containing C=C double bonds at neutral pH conditions.

Reactivity of ClO2 with Inorganic Compounds
ClO2 can oxidize many inorganic compounds, being first reduced to chlorite by the transfer of a single electron. In addition, chlorite can react with Fe(II) and Mn(II) [69][70][71][72]; the reactions [70,71] are summarized in Figure 24.

Reactivity of ClO 2
The chemistry of ClO 2 is complex compared to that of other chlorine compounds, because of its high reactivity. Chlorine dioxide is a strong oxidizing agent and, unlike chlorine, does not tend to react with organic materials to form chlorinated species, or with ammonia to form chloramine. The oxidation of ClO 2 generally begins with the removal of an electron from residual organic compounds to produce organic radicals and ClO 2 − . Subsequent oxidation of the organic radicals by ClO 2 involves oxygen transfer with the release of HOCl or electron transfer with the release of ClO 2 − [46,50]. Inorganic compounds are important in the body and are responsible for many simple functions. The major inorganic compounds are H 2 O, molecular oxygen O 2 , carbon dioxide CO 2 , and some acids, bases, and salts. Iron is a biologically essential component of every living organism and various cellular mechanisms have evolved to capture iron from the environment in biologically useful forms [60]. It is primarily involved in the transfer of oxygen from the lungs to tissues. However, iron also plays a role in metabolism as a component of some proteins and enzymes. Manganese (Mn) is a trace mineral that is present in tiny amounts in the body. It is found mostly in bones, the liver, kidneys, and pancreas, and helps the body form connective tissue, bones, blood clotting factors, and sex hormones. Manganese is a cofactor for many enzymes, including manganese superoxide dismutase, arginase, and pyruvate carboxylase. In these enzymes, manganese is involved in the metabolism of amino acids, cholesterol, glucose, and carbohydrates; the elimination of reactive oxygen species; bone formation; reproduction; immune response; and blood coagulation and hemostasis together with vitamin K [61][62][63][64][65][66][67].
Some researchers have studied the reactivity of ClO 2 with inorganic and organic compounds has been studied [68]. In the human body, ClO 2 can react with I − , NO 2 − , O 3 , H 2 O 2 , Fe(II), and Mn(II). The rate constants with tertiary amines and phenols were also high at pH ≥ 6. ClO 2 does not react with ammonia, Br − , carbohydrates, aromatic hydro-carbides, and compounds containing C=C double bonds at neutral pH conditions.

Reactivity of ClO 2 with Inorganic Compounds
ClO 2 can oxidize many inorganic compounds, being first reduced to chlorite by the transfer of a single electron. In addition, chlorite can react with Fe(II) and Mn(II) [69][70][71][72]; the reactions [70,71] are summarized in Figure 24. The degradation of ClO2 under UVC radiation accelerates the tendency of chlorite and chlorate formation compared to ClO2 alone. In addition, chlorite and chlorate can also be generated from radical-radical interactions [56][57][58][59], Figure 23.

Reactivity of ClO2
The chemistry of ClO2 is complex compared to that of other chlorine compounds, because of its high reactivity. Chlorine dioxide is a strong oxidizing agent and, unlike chlorine, does not tend to react with organic materials to form chlorinated species, or with ammonia to form chloramine. The oxidation of ClO2 generally begins with the removal of an electron from residual organic compounds to produce organic radicals and ClO2 − . Subsequent oxidation of the organic radicals by ClO2 involves oxygen transfer with the release of HOCl or electron transfer with the release of ClO2 − [46,50].
Inorganic compounds are important in the body and are responsible for many simple functions. The major inorganic compounds are H2O, molecular oxygen O2, carbon dioxide CO2, and some acids, bases, and salts. Iron is a biologically essential component of every living organism and various cellular mechanisms have evolved to capture iron from the environment in biologically useful forms [60]. It is primarily involved in the transfer of oxygen from the lungs to tissues. However, iron also plays a role in metabolism as a component of some proteins and enzymes. Manganese (Mn) is a trace mineral that is present in tiny amounts in the body. It is found mostly in bones, the liver, kidneys, and pancreas, and helps the body form connective tissue, bones, blood clotting factors, and sex hormones. Manganese is a cofactor for many enzymes, including manganese superoxide dismutase, arginase, and pyruvate carboxylase. In these enzymes, manganese is involved in the metabolism of amino acids, cholesterol, glucose, and carbohydrates; the elimination of reactive oxygen species; bone formation; reproduction; immune response; and blood coagulation and hemostasis together with vitamin K [61][62][63][64][65][66][67].
Some researchers have studied the reactivity of ClO2 with inorganic and organic compounds has been studied [68]. In the human body, ClO2 can react with I − , NO2 − , O3, H2O2, Fe(II), and Mn(II). The rate constants with tertiary amines and phenols were also high at pH ≥ 6. ClO2 does not react with ammonia, Br − , carbohydrates, aromatic hydro-carbides, and compounds containing C=C double bonds at neutral pH conditions.

Reactivity of ClO2 with Inorganic Compounds
ClO2 can oxidize many inorganic compounds, being first reduced to chlorite by the transfer of a single electron. In addition, chlorite can react with Fe(II) and Mn(II) [69][70][71][72]; the reactions [70,71] are summarized in Figure 24.  The reaction rate constants of the ClO 2 oxidation of Fe(II) and Mn(II) increase greatly with alkaline pH. Iodide, unlike bromide, is readily oxidized in the presence of ClO 2 to iodine. During oxidation of aqueous iodide, ClO 2 can rapidly oxidize I − to I 2 [73]. Chlorite [74,75] produced by the reduction of ClO 2 can also react with excess I − to form I 2 at pH 4-8 [76][77][78] (Figure 25). The reaction rate constants of the ClO2 oxidation of Fe(II) and Mn(II) increase greatly with alkaline pH. Iodide, unlike bromide, is readily oxidized in the presence of ClO2 to iodine. During oxidation of aqueous iodide, ClO2 can rapidly oxidize I − to I2 [73]. Chlo rite [74,75] produced by the reduction of ClO2 can also react with excess I − to form I2 at pH 4-8 [76][77][78] (Figure 25).  Chlorite can be further reduced to chloride through reactions with CN − and NO2 − . In the following reaction shown in Figure 27, H2O2 acts as a reducing agent [8]. In the reaction with O3, ClO2 is the reducing agent ( Figure 28).

Reactivity with Organic Compounds
The reactions of ClO2 with organic compounds have generally been investigated in aqueous solutions with low reagent concentrations, in which it reacts with humic and ful vic acids present in water, forming oxidized organic compounds, such as aldehydes and carboxylic acids. It does not form chlorinated organic by-products unless free chlorine i present together with chlorine dioxide.
ClO2 reacts with phenolic groups, sulfur compounds, and to a lesser extent, tertiary amines and aromatic amines, while the reaction with hydrocarbons is practically nil. The reactivity of the phenoxide ion and the neutral form of the amine is much greater (by several orders of magnitude) than the reactivity of the neutral form of the phenol and the protonated amine. ClO2 tends to react with organic compounds as an electron accepto and is reduced to chlorite. This makes ClO2 a selective oxidant whose reactivity generally favors organic molecules with a lone pair of electrons.

Reactivity with Phenolic Compounds
Chlorine dioxide oxidizes phenolic compounds and has been used to oxidize chlo rinated phenolic compounds to reduce their toxicity. At neutral pH, phenols react with ClO2 with values between 10 3 -10 8 M −1 s −1 . The reaction rate constants of phenols dissoci ated with ClO2 are generally six orders of magnitude higher than those of undissociated phenols [79] (Table 1). Therefore, at high pH, the oxidation of phenols with ClO2 is favored The substituents of phenols greatly affect their oxidation rates with ClO2. The nitrite ion is oxidized to nitrate in the presence of ClO 2 . Like iodide, the oxidation of nitrite (NO 2 − ) by ClO 2 involves mainly electron transfer reactions ( Figure 26). The reaction rate constants of the ClO2 oxidation of Fe(II) and Mn(II) increase greatl with alkaline pH. Iodide, unlike bromide, is readily oxidized in the presence of ClO2 t iodine. During oxidation of aqueous iodide, ClO2 can rapidly oxidize I − to I2 [73]. Chlo rite [74,75] produced by the reduction of ClO2 can also react with excess I − to form I2 at pH 4-8 [76][77][78] (Figure 25).  Chlorite can be further reduced to chloride through reactions with CN − and NO2 − . I the following reaction shown in Figure 27, H2O2 acts as a reducing agent [8]. In the reaction with O3, ClO2 is the reducing agent ( Figure 28).

Reactivity with Organic Compounds
The reactions of ClO2 with organic compounds have generally been investigated i aqueous solutions with low reagent concentrations, in which it reacts with humic and ful vic acids present in water, forming oxidized organic compounds, such as aldehydes and carboxylic acids. It does not form chlorinated organic by-products unless free chlorine i present together with chlorine dioxide.
ClO2 reacts with phenolic groups, sulfur compounds, and to a lesser extent, tertiar amines and aromatic amines, while the reaction with hydrocarbons is practically nil. Th reactivity of the phenoxide ion and the neutral form of the amine is much greater (b several orders of magnitude) than the reactivity of the neutral form of the phenol and th protonated amine. ClO2 tends to react with organic compounds as an electron accepto and is reduced to chlorite. This makes ClO2 a selective oxidant whose reactivity generall favors organic molecules with a lone pair of electrons.

Reactivity with Phenolic Compounds
Chlorine dioxide oxidizes phenolic compounds and has been used to oxidize chlo rinated phenolic compounds to reduce their toxicity. At neutral pH, phenols react wit ClO2 with values between 10 3 -10 8 M −1 s −1 . The reaction rate constants of phenols dissoci ated with ClO2 are generally six orders of magnitude higher than those of undissociated phenols [79] (Table 1). Therefore, at high pH, the oxidation of phenols with ClO2 is favored The substituents of phenols greatly affect their oxidation rates with ClO2. Chlorite can be further reduced to chloride through reactions with CN − and NO 2 − . In the following reaction shown in Figure 27, H 2 O 2 acts as a reducing agent [8]. The reaction rate constants of the ClO2 oxidation of Fe(II) and Mn(II) increase greatl with alkaline pH. Iodide, unlike bromide, is readily oxidized in the presence of ClO2 t iodine. During oxidation of aqueous iodide, ClO2 can rapidly oxidize I − to I2 [73]. Chlo rite [74,75] produced by the reduction of ClO2 can also react with excess I − to form I2 at pH 4-8 [76][77][78] (Figure 25).  Chlorite can be further reduced to chloride through reactions with CN − and NO2 − . I the following reaction shown in Figure 27, H2O2 acts as a reducing agent [8]. In the reaction with O3, ClO2 is the reducing agent ( Figure 28).

Reactivity with Organic Compounds
The reactions of ClO2 with organic compounds have generally been investigated i aqueous solutions with low reagent concentrations, in which it reacts with humic and fu vic acids present in water, forming oxidized organic compounds, such as aldehydes an carboxylic acids. It does not form chlorinated organic by-products unless free chlorine i present together with chlorine dioxide.
ClO2 reacts with phenolic groups, sulfur compounds, and to a lesser extent, tertiar amines and aromatic amines, while the reaction with hydrocarbons is practically nil. Th reactivity of the phenoxide ion and the neutral form of the amine is much greater (b several orders of magnitude) than the reactivity of the neutral form of the phenol and th protonated amine. ClO2 tends to react with organic compounds as an electron accepto and is reduced to chlorite. This makes ClO2 a selective oxidant whose reactivity generall favors organic molecules with a lone pair of electrons.

Reactivity with Phenolic Compounds
Chlorine dioxide oxidizes phenolic compounds and has been used to oxidize chlo rinated phenolic compounds to reduce their toxicity. At neutral pH, phenols react wit ClO2 with values between 10 3 -10 8 M −1 s −1 . The reaction rate constants of phenols dissoc ated with ClO2 are generally six orders of magnitude higher than those of undissociate phenols [79] (Table 1). Therefore, at high pH, the oxidation of phenols with ClO2 is favored The substituents of phenols greatly affect their oxidation rates with ClO2. In the reaction with O 3 , ClO 2 is the reducing agent ( Figure 28).
The reaction rate constants of the ClO2 oxidation of Fe(II) and Mn(II) increase greatl with alkaline pH. Iodide, unlike bromide, is readily oxidized in the presence of ClO2 t iodine. During oxidation of aqueous iodide, ClO2 can rapidly oxidize I − to I2 [73]. Chlo rite [74,75] produced by the reduction of ClO2 can also react with excess I − to form I2 at pH 4-8 [76][77][78] (Figure 25).  Chlorite can be further reduced to chloride through reactions with CN − and NO2 − . In the following reaction shown in Figure 27, H2O2 acts as a reducing agent [8]. In the reaction with O3, ClO2 is the reducing agent ( Figure 28).

Reactivity with Organic Compounds
The reactions of ClO2 with organic compounds have generally been investigated in aqueous solutions with low reagent concentrations, in which it reacts with humic and ful vic acids present in water, forming oxidized organic compounds, such as aldehydes and carboxylic acids. It does not form chlorinated organic by-products unless free chlorine i present together with chlorine dioxide.
ClO2 reacts with phenolic groups, sulfur compounds, and to a lesser extent, tertiar amines and aromatic amines, while the reaction with hydrocarbons is practically nil. Th reactivity of the phenoxide ion and the neutral form of the amine is much greater (b several orders of magnitude) than the reactivity of the neutral form of the phenol and th protonated amine. ClO2 tends to react with organic compounds as an electron accepto and is reduced to chlorite. This makes ClO2 a selective oxidant whose reactivity generall favors organic molecules with a lone pair of electrons.

Reactivity with Phenolic Compounds
Chlorine dioxide oxidizes phenolic compounds and has been used to oxidize chlo rinated phenolic compounds to reduce their toxicity. At neutral pH, phenols react with ClO2 with values between 10 3 -10 8 M −1 s −1 . The reaction rate constants of phenols dissoci ated with ClO2 are generally six orders of magnitude higher than those of undissociated phenols [79] (Table 1). Therefore, at high pH, the oxidation of phenols with ClO2 is favored The substituents of phenols greatly affect their oxidation rates with ClO2.

Reactivity with Organic Compounds
The reactions of ClO 2 with organic compounds have generally been investigated in aqueous solutions with low reagent concentrations, in which it reacts with humic and fulvic acids present in water, forming oxidized organic compounds, such as aldehydes and carboxylic acids. It does not form chlorinated organic by-products unless free chlorine is present together with chlorine dioxide. ClO 2 reacts with phenolic groups, sulfur compounds, and to a lesser extent, tertiary amines and aromatic amines, while the reaction with hydrocarbons is practically nil. The reactivity of the phenoxide ion and the neutral form of the amine is much greater (by several orders of magnitude) than the reactivity of the neutral form of the phenol and the protonated amine. ClO 2 tends to react with organic compounds as an electron acceptor and is reduced to chlorite. This makes ClO 2 a selective oxidant whose reactivity generally favors organic molecules with a lone pair of electrons.

Reactivity with Phenolic Compounds
Chlorine dioxide oxidizes phenolic compounds and has been used to oxidize chlorinated phenolic compounds to reduce their toxicity. At neutral pH, phenols react with ClO 2 with values between 10 3 -10 8 M −1 s −1 . The reaction rate constants of phenols dissociated with ClO 2 are generally six orders of magnitude higher than those of undissociated phenols [79] (Table 1). Therefore, at high pH, the oxidation of phenols with ClO 2 is favored. The substituents of phenols greatly affect their oxidation rates with ClO 2 . The main products of the oxidation of phenols with chlorine dioxide are p-benzoquinone and various substituted chloro-p-benzoquinones [80]. The chlorophenols are oxidized to the corresponding quinones. With a large excess of ClO 2 , the p-quinone is oxidized with ring cleavage, forming dicarboxylic acids. Oxidation of phenols and chloro-phenols [81] is shown in Figure 29.  The main products of the oxidation of phenols with chlorine dioxide are p-benzoquinone and various substituted chloro-p-benzoquinones [80]. The chlorophenols are oxidized to the corresponding quinones. With a large excess of ClO2, the p-quinone is oxidized with ring cleavage, forming dicarboxylic acids. Oxidation of phenols and chlorophenols [81] is shown in Figure 29. This is a two-step mechanism: ClO2 reacts with a phenoxide ion that is stabilized to ClO2 − and a phenoxy radical. This radical reacts rapidly with a second equivalent of ClO2 to produce p-benzoquinone and release HOCl. In this mechanism, it was suggested that a phenoxy radical and ClO2 radical intermediate could be formed [82] (Figure 30).  This is a two-step mechanism: ClO 2 reacts with a phenoxide ion that is stabilized to ClO 2 − and a phenoxy radical. This radical reacts rapidly with a second equivalent of ClO 2 to produce p-benzoquinone and release HOCl. In this mechanism, it was suggested that a phenoxy radical and ClO 2 radical intermediate could be formed [82] (Figure 30).  The main products of the oxidation of phenols with chlorine dioxide are p-benzoquinone and various substituted chloro-p-benzoquinones [80]. The chlorophenols are oxidized to the corresponding quinones. With a large excess of ClO2, the p-quinone is oxidized with ring cleavage, forming dicarboxylic acids. Oxidation of phenols and chlorophenols [81] is shown in Figure 29. This is a two-step mechanism: ClO2 reacts with a phenoxide ion that is stabilized to ClO2 − and a phenoxy radical. This radical reacts rapidly with a second equivalent of ClO2 to produce p-benzoquinone and release HOCl. In this mechanism, it was suggested that a phenoxy radical and ClO2 radical intermediate could be formed [82] (Figure 30).  Chlorinated derivatives in the oxidations of phenols with ClO 2 can be explained by the hypochlorous acid formed in the reaction [83] (Figure 31).

Reactivity with Aromatic Amines
Aromatic amines are widely distributed in aqueous media, sometimes as degradation products of herbicides (in agriculture) or dyes in industrial wastewater [84].
The mechanism of ClO2 oxidation of aniline begins with an electron transfer in the first step. The amino group is directly attached to a benzene ring (and is a high electron density center), so there is a change in the electron density of the nitrogen atom as it gives up charge to the benzene ring. The reaction pathways and products obtained are different from those observed with aliphatic amines. The main product obtained is the quinoneazobenzene derivative ( Figure 32).

Reactivity with Aliphatic Amines
Aliphatic amines are widely distributed in aqueous media, and they react quickly with ClO2 to form freely available chlorine FAC [85]. Second-order rate constants for reactions of chlorine dioxide with aliphatic amines in aqueous solutions are listed in Table 2. Tertiary amines react with ClO2 very quickly; secondary and especially primary amines react much more slowly, and ammonia does not react with ClO2 at all [80,87].
ClO2 oxidizes most aliphatic tertiary amines rapidly and converts them to secondary amines, also forming aldehydes. The possible mechanism is the formation of an aminyl Aromatic amines are widely distributed in aqueous media, sometimes as degradation products of herbicides (in agriculture) or dyes in industrial wastewater [84].
The mechanism of ClO 2 oxidation of aniline begins with an electron transfer in the first step. The amino group is directly attached to a benzene ring (and is a high electron density center), so there is a change in the electron density of the nitrogen atom as it gives up charge to the benzene ring. The reaction pathways and products obtained are different from those observed with aliphatic amines. The main product obtained is the quinone-azobenzene derivative ( Figure 32).

Reactivity with Aromatic Amines
Aromatic amines are widely distributed in aqueous media, sometimes as degradation products of herbicides (in agriculture) or dyes in industrial wastewater [84].
The mechanism of ClO2 oxidation of aniline begins with an electron transfer in the first step. The amino group is directly attached to a benzene ring (and is a high electron density center), so there is a change in the electron density of the nitrogen atom as it gives up charge to the benzene ring. The reaction pathways and products obtained are different from those observed with aliphatic amines. The main product obtained is the quinoneazobenzene derivative ( Figure 32).

Reactivity with Aliphatic Amines
Aliphatic amines are widely distributed in aqueous media, and they react quickly with ClO2 to form freely available chlorine FAC [85]. Second-order rate constants for reactions of chlorine dioxide with aliphatic amines in aqueous solutions are listed in Table 2. Tertiary amines react with ClO2 very quickly; secondary and especially primary amines react much more slowly, and ammonia does not react with ClO2 at all [80,87].
ClO2 oxidizes most aliphatic tertiary amines rapidly and converts them to secondary amines, also forming aldehydes. The possible mechanism is the formation of an aminyl

Reactivity with Aliphatic Amines
Aliphatic amines are widely distributed in aqueous media, and they react quickly with ClO 2 to form freely available chlorine FAC [85]. Second-order rate constants for reactions of chlorine dioxide with aliphatic amines in aqueous solutions are listed in Table 2. Tertiary amines react with ClO 2 very quickly; secondary and especially primary amines react much more slowly, and ammonia does not react with ClO 2 at all [80,87].
ClO 2 oxidizes most aliphatic tertiary amines rapidly and converts them to secondary amines, also forming aldehydes. The possible mechanism is the formation of an aminyl cation radical and chlorite followed by the elimination of a proton at alpha, forming an amine thatsubsequently hydrolyses to the aldehyde and secondary amine [8].

Reactivity with Amino Acids, Peptides, and Proteins
Reaction rates with amines decrease in the order tertiary amine > secondary amine > primary amine. For tertiary amines, the reaction rate constants are in the range 10 3 -10 6 M −1 s −1 at neutral pH and are between 2-5 orders of magnitude higher than for secondary or primary amines. ClO 2 reacts much faster with deprotonated amines than with neutral species because deprotonated amines are stronger electron donors [90,91].
The reactivity of ClO 2 with biologically important molecules (including amino acids and some peptides) has been well studied [92,93]. ClO 2 is an effective and promising alternative to other chlorine-containing disinfectants, and a thorough understanding of the chemistry of interactions with amino acids, proteins, and peptides is needed.
ClO 2 reacts rapidly with cysteine, tyrosine, and tryptophan (10 4 -10 7 M −1 s −1 ), but slowly with histidine, proline, alanine, and glycine (10 −5 -10 −2 M −1 s −1 ) [93]. Amino acids have a primary amine in their structure; this amino group is not reactive with ClO 2 . Amino acids reactive with ClO 2 contain other reactive groups such as phenols or sulfur groups. The following order of reactivity has been reported (Figures 33 and 34). Mol. Sci. 2022, 23, 15660 14 of 28 cation radical and chlorite followed by the elimination of a proton at alpha, forming an amine thatsubsequently hydrolyses to the aldehyde and secondary amine [8].

Reactivity with Amino Acids, Peptides, and Proteins
Reaction rates with amines decrease in the order tertiary amine > secondary amine > primary amine. For tertiary amines, the reaction rate constants are in the range 10 3 -10 6 M −1 s −1 at neutral pH and are between 2-5 orders of magnitude higher than for secondary or primary amines. ClO2 reacts much faster with deprotonated amines than with neutral species because deprotonated amines are stronger electron donors [90,91].
The reactivity of ClO2 with biologically important molecules (including amino acids and some peptides) has been well studied [92,93]. ClO2 is an effective and promising alternative to other chlorine-containing disinfectants, and a thorough understanding of the chemistry of interactions with amino acids, proteins, and peptides is needed.
ClO2 reacts rapidly with cysteine, tyrosine, and tryptophan (10 4 -10 7 M −1 s −1 ), but slowly with histidine, proline, alanine, and glycine (10 −5 -10 −2 M −1 s −1 ) [93]. Amino acids have a primary amine in their structure; this amino group is not reactive with ClO2. Amino acids reactive with ClO2 contain other reactive groups such as phenols or sulfur groups. The following order of reactivity has been reported (Figures 33 and 34). Cysteine, due to its nucleophilic -SH group, is the most reactive amino acid with ClO2 [94]. Oxidation of cysteine by ClO2 has been studied in detail, determining the stoichiometry and reaction products [95]. The stoichiometry of the reaction ([ClO2]:[Cys]) was found to be pH-dependent, being 1:0.9 in acidic media and 1:3.7 in basic media ( Figure  35). Int. J. Mol. Sci. 2022, 23, 15660 14 of 2 cation radical and chlorite followed by the elimination of a proton at alpha, forming an amine thatsubsequently hydrolyses to the aldehyde and secondary amine [8].

Reactivity with Amino Acids, Peptides, and Proteins
Reaction rates with amines decrease in the order tertiary amine > secondary amine > primary amine. For tertiary amines, the reaction rate constants are in the range 10 3 -10 6 M − s −1 at neutral pH and are between 2-5 orders of magnitude higher than for secondary o primary amines. ClO2 reacts much faster with deprotonated amines than with neutral spe cies because deprotonated amines are stronger electron donors [90,91].
The reactivity of ClO2 with biologically important molecules (including amino acid and some peptides) has been well studied [92,93]. ClO2 is an effective and promising alter native to other chlorine-containing disinfectants, and a thorough understanding of the chemistry of interactions with amino acids, proteins, and peptides is needed.
ClO2 reacts rapidly with cysteine, tyrosine, and tryptophan (10 4 -10 7 M −1 s −1 ), bu slowly with histidine, proline, alanine, and glycine (10 −5 -10 −2 M −1 s −1 ) [93]. Amino acid have a primary amine in their structure; this amino group is not reactive with ClO2. Amino acids reactive with ClO2 contain other reactive groups such as phenols or sulfur groups The following order of reactivity has been reported (Figures 33 and 34). Cysteine, due to its nucleophilic -SH group, is the most reactive amino acid with ClO2 [94]. Oxidation of cysteine by ClO2 has been studied in detail, determining the stoi chiometry and reaction products [95]. The stoichiometry of the reaction ([ClO2]:[Cys]) wa found to be pH-dependent, being 1:0.9 in acidic media and 1:3.7 in basic media (Figur 35). Cysteine, due to its nucleophilic -SH group, is the most reactive amino acid with ClO 2 [94]. Oxidation of cysteine by ClO 2 has been studied in detail, determining the stoichiometry and reaction products [95]. The stoichiometry of the reaction ([ClO 2 ]: [Cys]) was found to be pH-dependent, being 1:0.9 in acidic media and 1:3.7 in basic media ( Figure 35). At acidic pH, cysteine sulphonic acid was produced, while at alkaline pH, cystine was obtained, which are products of the oxidation of cysteine by ClO2 (Figure 36). The reactive cysteine species is the thiolate ion, and it is proposed that the rate-determining step involves electron abstraction from the thiolate ion by ClO2 to give the cysteinyl radical. This radical reacts rapidly with another ClO2 molecule to form a cysteinyl-ClO2 adduct, which is disproportionated by two pH-dependent pathways to produce cystine and cysteic acid ( Figure 37). The reactivity of glutathione is like that of cysteine, and similar steps in the reaction with ClO2 are proposed. A study of the oxidation of thiols (Cys and GSH) by ClO2 with varying pH has been performed. The rate constant for Cys and GSH increased with pH from 3.2 to 5.9. The pH-dependent behavior suggests that deprotonated thiols are the reactive species. The rate constants [94,95]   At acidic pH, cysteine sulphonic acid was produced, while at alkaline pH, cystine was obtained, which are products of the oxidation of cysteine by ClO 2 (Figure 36). At acidic pH, cysteine sulphonic acid was produced, while at alkaline pH, cystine was obtained, which are products of the oxidation of cysteine by ClO2 (Figure 36). The reactive cysteine species is the thiolate ion, and it is proposed that the rate-determining step involves electron abstraction from the thiolate ion by ClO2 to give the cysteinyl radical. This radical reacts rapidly with another ClO2 molecule to form a cysteinyl-ClO2 adduct, which is disproportionated by two pH-dependent pathways to produce cystine and cysteic acid ( Figure 37). The reactivity of glutathione is like that of cysteine, and similar steps in the reaction with ClO2 are proposed. A study of the oxidation of thiols (Cys and GSH) by ClO2 with varying pH has been performed. The rate constant for Cys and GSH increased with pH from 3.2 to 5.9. The pH-dependent behavior suggests that deprotonated thiols are the reactive species. The rate constants [94,95]   The reactive cysteine species is the thiolate ion, and it is proposed that the ratedetermining step involves electron abstraction from the thiolate ion by ClO 2 to give the cysteinyl radical. This radical reacts rapidly with another ClO 2 molecule to form a cysteinyl-ClO 2 adduct, which is disproportionated by two pH-dependent pathways to produce cystine and cysteic acid ( Figure 37). At acidic pH, cysteine sulphonic acid was produced, while at alkaline pH, cystine was obtained, which are products of the oxidation of cysteine by ClO2 (Figure 36). The reactive cysteine species is the thiolate ion, and it is proposed that the rate-determining step involves electron abstraction from the thiolate ion by ClO2 to give the cysteinyl radical. This radical reacts rapidly with another ClO2 molecule to form a cysteinyl-ClO2 adduct, which is disproportionated by two pH-dependent pathways to produce cystine and cysteic acid ( Figure 37). The reactivity of glutathione is like that of cysteine, and similar steps in the reaction with ClO2 are proposed. A study of the oxidation of thiols (Cys and GSH) by ClO2 with varying pH has been performed. The rate constant for Cys and GSH increased with pH from 3.2 to 5.9. The pH-dependent behavior suggests that deprotonated thiols are the reactive species. The rate constants [94,95]   The reactivity of glutathione is like that of cysteine, and similar steps in the reaction with ClO 2 are proposed. A study of the oxidation of thiols (Cys and GSH) by ClO 2 with varying pH has been performed. The rate constant for Cys and GSH increased with pH from 3.2 to 5.9. The pH-dependent behavior suggests that deprotonated thiols are the reactive species. The rate constants [94,95] for the reactions of ClO 2 with cysteinyl anion (CS − ) and glutathione anion (GS − ) are 1.0 × 10 8 M −1 s −1 and 1.4 × 10 8 M −1 s −1 , respectively. Similar rate constants suggest common oxidation mechanisms for cysteine and glutathione by ClO 2 .
In the reactions of histidine, tryptophan, and tyrosine with ClO 2 , different products are obtained depending on the molar ratios of ClO 2 . The products also vary if the reaction is done in the presence or absence of oxygen. With an excess of ClO 2 , low molecular weight compounds are obtained.
ClO 2 oxidation of tyrosine occurs predominantly in its phenolic structure, resulting in the formation of dopaquinone and dopachrome at pH 6-7. Cyclisation of dopaquinone occurred at pH > 4 to form cyclodopa, which was subsequently oxidized to dopachrome [96] (Figure 38). Int. J. Mol. Sci. 2022, 23, 15660 16 of 28 rate constants suggest common oxidation mechanisms for cysteine and glutathione by ClO2.
In the reactions of histidine, tryptophan, and tyrosine with ClO2, different products are obtained depending on the molar ratios of ClO2. The products also vary if the reaction is done in the presence or absence of oxygen. With an excess of ClO2, low molecular weight compounds are obtained.
ClO2 oxidation of tyrosine occurs predominantly in its phenolic structure, resulting in the formation of dopaquinone and dopachrome at pH 6-7. Cyclisation of dopaquinone occurred at pH > 4 to form cyclodopa, which was subsequently oxidized to dopachrome [96] (Figure 38). The product of tryptophan oxidation by ClO2 was identified as N-formyl alkyl-nurenine [97]. The initial reaction between tryptophan and ClO2 is a one-electron oxidation to form a tryptophan radical cation and a chlorite ion. The radical cation deprotonates to form a neutral tryptophilic radical, which reacts rapidly with a second ClO2 molecule to give a short-lived adduct (kobs = 48 s −1 ) with formation of the C-OClO bond. This adduct decomposes to give HOCl [8] (Figure 39). The product of tryptophan oxidation by ClO 2 was identified as N-formyl alkylnurenine [97]. The initial reaction between tryptophan and ClO 2 is a one-electron oxidation to form a tryptophan radical cation and a chlorite ion. The radical cation deprotonates to form a neutral tryptophilic radical, which reacts rapidly with a second ClO 2 molecule to give a short-lived adduct (k obs = 48 s −1 ) with formation of the C-OClO bond. This adduct decomposes to give HOCl [8] (Figure 39).   The reaction consumes two ClO2 per Trp and forms chlorite and HOCl ( Figure 40). Figure 40. Stoichiometry of the reaction between tryptophan and ClO2.

Oxidation of Peptides and Proteins by ClO2
ClO2 is a selective oxidant that only reacts with five amino acids: cysteine, tyrosine, tryptophan, histidine, and proline. Cysteine, tyrosine, and tryptophan have much faster reaction rate constants. Mass spectrometry and nuclear magnetic resonance spectroscopy show that tryptophan residues are converted to N-formyl alkyl-nurenine and tyrosine residues are converted to 3,4-dihydroxyphenylalanine (DOPA) or 2,4,5-trihydroxyphenylalanine (TOPA) in ClO2-treated proteins. Tryptophan residues are critical targets in the reaction between ClO2 and proteins [98,99], causing protein fragmentation and denaturation. Inactivation of influenza A virus when treated with ClO2 has been observed due to oxidation of a tryptophan residue (W 153 ) that was converted to NFK in hemagglutinin, restricting its ability to bind to host cells [100].
Using bovine serum albumin and glucose-6-phosphate dehydrogenase (G6PD) from baker's yeast (Saccharomyces cerevisiae) as model proteins, it was shown that the antimicrobial activity of ClO2 is mainly attributed to its protein denaturing activity. Elemental analyses show that oxygen atoms, but not chlorine atoms, are incorporated into the ClO2treated protein, providing direct evidence that ClO2 oxidizes the protein. For glutathione, a tripeptide consisting of glycine, cysteine, and glutamic acid, the ClO2-reactive site is the thiol group, and the oxidation products are like those of cysteine (Table 3).

Oxidation of Peptides and Proteins by ClO 2
ClO 2 is a selective oxidant that only reacts with five amino acids: cysteine, tyrosine, tryptophan, histidine, and proline. Cysteine, tyrosine, and tryptophan have much faster reaction rate constants. Mass spectrometry and nuclear magnetic resonance spectroscopy show that tryptophan residues are converted to N-formyl alkyl-nurenine and tyrosine residues are converted to 3,4-dihydroxyphenylalanine (DOPA) or 2,4,5trihydroxyphenylalanine (TOPA) in ClO 2 -treated proteins. Tryptophan residues are critical targets in the reaction between ClO 2 and proteins [98,99], causing protein fragmentation and denaturation. Inactivation of influenza A virus when treated with ClO 2 has been observed due to oxidation of a tryptophan residue (W 153 ) that was converted to NFK in hemagglutinin, restricting its ability to bind to host cells [100].
Using bovine serum albumin and glucose-6-phosphate dehydrogenase (G6PD) from baker's yeast (Saccharomyces cerevisiae) as model proteins, it was shown that the antimicrobial activity of ClO 2 is mainly attributed to its protein denaturing activity. Elemental analyses show that oxygen atoms, but not chlorine atoms, are incorporated into the ClO 2treated protein, providing direct evidence that ClO 2 oxidizes the protein. For glutathione, a tripeptide consisting of glycine, cysteine, and glutamic acid, the ClO 2 -reactive site is the thiol group, and the oxidation products are like those of cysteine (Table 3).

Oxidation of NADH by Chlorine Dioxide
The oxidation of dihydronicotinamide adenine dinucleotide (NADH) by chlorine dioxide in phosphate-buffered solutions (pH 6-8) is very fast, with a second-order rate constant of 3.9 × 10 6 M −1 s −1 at 24.6 • C. The stoichiometry is shown in Figure 41.

Oxidation of NADH by Chlorine Dioxide
The oxidation of dihydronicotinamide adenine dinucleotide (NADH) by chlorine dioxide in phosphate-buffered solutions (pH 6-8) is very fast, with a second-order rate constant of 3.9 × 10 6 M −1 s −1 at 24.6 °C. The stoichiometry is shown in Figure 41. Unlike many oxidants in which NADH reacts by hydride transfer, the proposed mechanism is a one-electron transfer from NADH to ClO2. First, chlorine dioxide accepts an electron from NADH to form ClO2 − and the radical cation NADH + . Then, the subsequent sequence of very rapid deprotonation with the transfer of H + to H2O and the transfer of an electron to a second equivalent of ClO2 gives as products 2ClO2 − , H3O + , and NAD+ [101] (Figure 42). Unlike many oxidants in which NADH reacts by hydride transfer, the proposed mechanism is a one-electron transfer from NADH to ClO 2 . First, chlorine dioxide accepts an electron from NADH to form ClO 2 − and the radical cation NADH + . Then, the subsequent sequence of very rapid deprotonation with the transfer of H + to H 2 O and the transfer of an electron to a second equivalent of ClO 2 gives as products 2ClO 2 − , H 3 O + , and NAD+ [101] (Figure 42). Unlike many oxidants in which NADH reacts by hydride transfer, the proposed mechanism is a one-electron transfer from NADH to ClO2. First, chlorine dioxide accepts an electron from NADH to form ClO2 − and the radical cation NADH + . Then, the subsequent sequence of very rapid deprotonation with the transfer of H + to H2O and the transfer of an electron to a second equivalent of ClO2 gives as products 2ClO2 − , H3O + , and NAD+ [101] (Figure 42). The mechanism by which ClO2 influences biomolecules is based on the strong interference with redox processes occurring in mitochondrial and cell membranes, e.g., on the NADH/NAD + system, which is responsible for cellular respiration and for mediating ATP synthesis [102].

Oxidation of Hemoglobin by ClO2
Chlorine dioxide is an oxidizing agent that converts hemoglobin (oxygen-carrying protein) into methemoglobin, which cannot bind to other oxygen molecules and therefore hinders oxygenation of the body. In these cases, as when ingested in large quantities, ClO2 oxidizes ferrous iron (Fe 2+ ) and transforms it into ferric iron (Fe 3+ ), and hemoglobin becomes methemoglobin, which causes respiratory failure [33].
Methemoglobin is an oxidized form of hemoglobin that is unable to carry oxygen in the blood and is therefore unable to release it effectively into the body's tissues, thus preventing oxygenation of the body. High levels of methemoglobin can have other risks. Methemoglobin-forming chemicals can oxidate the ferrous nucleus of hemoglobin (Fe 2+ ) into trivalent iron (Fe 3+ ), transforming hemoglobin into methemoglobin. Its toxic effects are due to the reduced oxygen-carrying capacity of methemoglobin, resulting in cellular hypoxia [103,104] (Figure 43). The mechanism by which ClO 2 influences biomolecules is based on the strong interference with redox processes occurring in mitochondrial and cell membranes, e.g., on the NADH/NAD + system, which is responsible for cellular respiration and for mediating ATP synthesis [102].

Oxidation of Hemoglobin by ClO 2
Chlorine dioxide is an oxidizing agent that converts hemoglobin (oxygen-carrying protein) into methemoglobin, which cannot bind to other oxygen molecules and therefore hinders oxygenation of the body. In these cases, as when ingested in large quantities, ClO 2 oxidizes ferrous iron (Fe 2+ ) and transforms it into ferric iron (Fe 3+ ), and hemoglobin becomes methemoglobin, which causes respiratory failure [33].
Methemoglobin is an oxidized form of hemoglobin that is unable to carry oxygen in the blood and is therefore unable to release it effectively into the body's tissues, thus preventing oxygenation of the body. High levels of methemoglobin can have other risks. Methemoglobin-forming chemicals can oxidate the ferrous nucleus of hemoglobin (Fe 2+ ) into trivalent iron (Fe 3+ ), transforming hemoglobin into methemoglobin. Its toxic effects are due to the reduced oxygen-carrying capacity of methemoglobin, resulting in cellular hypoxia [103,104] (Figure 43). In 2015, the first case of a child with methemoglobinemia (high methemoglobin levels) after accidentally ingesting chlorine dioxide appeared in the literature. The authors reported that "the patient had profound hypoxia, did not respond to oxygen therapy, and required endotracheal intubation to maintain a normal oxygen level" [105].
In another publication in 2013, a person who tried to commit suicide and ingested less than 100 mL of a 28% sodium chlorite solution had 40% methemoglobin in his blood, requiring a kidney transplant and transfusions to save his life [106].
For these reasons, specialists conclude that chlorine dioxide not only deoxygenates the body, it can cause low tissue oxygenation capacity even in small doses, a situation that can put people's lives at risk.

Toxicity of ClO2
In  In 2015, the first case of a child with methemoglobinemia (high methemoglobin levels) after accidentally ingesting chlorine dioxide appeared in the literature. The authors reported that "the patient had profound hypoxia, did not respond to oxygen therapy, and required endotracheal intubation to maintain a normal oxygen level" [105].
In another publication in 2013, a person who tried to commit suicide and ingested less than 100 mL of a 28% sodium chlorite solution had 40% methemoglobin in his blood, requiring a kidney transplant and transfusions to save his life [106].
For these reasons, specialists conclude that chlorine dioxide not only deoxygenates the body, it can cause low tissue oxygenation capacity even in small doses, a situation that can put people's lives at risk.

Toxicity of ClO 2
In December 2019, a new respiratory illness emerged in Wuhan, China. The source of this infection was identified as a new coronavirus, related to other coronaviruses that had previously caused outbreaks of SARS (Severe Acute Respiratory Syndrome) between 2002 and 2004 and MERS (Middle East Respiratory Syndrome) in 2012 (National Institutes of Health, 2020). This virus was named "severe acute respiratory syndrome coronavirus 2" (SARS-CoV-2) and the disease resulting from infection with this virus was named "COVID-19". On 11 March 2020, the World Health Organization WHO declared COVID-19 a pandemic. Coronaviruses are a group of enveloped RNA viruses that can damage multiple organ systems. Like other coronaviruses, SARS-CoV-2 is a spherical particle with glycoprotein spikes on its surface. Coronaviruses enter host cells when a region of the spike, known as the "receptor-binding domain", binds to angiotensin-converting enzyme 2 (hACE2) in human cells. The viral membrane then fuses with the host cell membrane, allowing the viral genome to enter the host cell.
During the COVID-19 pandemic, the consumption of chlorine dioxide solutions has been promoted through different avenues (social networks, websites, mass media) for the treatment or prevention of SARS-CoV-2 infection. Different regulatory agencies (such as the European Medicines Agency and the US Food and Drug Administration) and scientific societies have drafted and issued statements warning about the lack of scientific evidence for their efficacy in COVID-19 disease and the associated risks to human health, and even demanded the withdrawal of these products from the market.
The FDA (Food and Drug Administration) in the United States of America and COFEPRIS (Comisión Federal para la Protección contra Riesgos Sanitarios) in Mexico state that the consumption of ClO 2 causes kidney and liver failure and destroys red blood cells. To date, there is no scientific evidence to support the use of chlorine dioxide or chlorine derivatives as preventive or therapeutic agents against COVID-19 [107][108][109].
Studies have described the toxic effects of chlorine dioxide ingestion. The main routes of intoxication can be divided into three: inhalation, oral, and parenteral routes ( Figure 44). Studies have described the toxic effects of chlorine dioxide ingestion. The main routes of intoxication can be divided into three: inhalation, oral, and parenteral routes ( Figure  44). Chlorine dioxide can be rapidly absorbed through the gastrointestinal tract. Peak blood concentration levels can be reached within 1 h after a single dose administered orally. It can also be absorbed slowly through shaved skin with a median absorption time of 22 h. Intact chlorine dioxide is unlikely to be absorbed by inhalation given its highly reactive nature; it is more likely that its derivatives can be absorbed. Chlorine dioxide is metabolized to chlorite, chlorate, and mainly chloride. Most of the administered chlorine dioxide and its metabolites remain in the plasma, followed by the kidneys, lungs, stomach, intestine, liver, and spleen. About 43% of orally administered chlorine dioxide is excreted in the urine and feces within 72 h.
It is important to note that neither chlorine dioxide nor its derivatives have undergone any evaluation or authorization by the competent authorities to ensure that the benefit/risk ratio is positive for the population.
There is no published scientific evidence that has positively considered the use of chlorine dioxide or its derivatives as a preventive or therapeutic agent against COVID-19 administered by inhalation, oral, or parenteral routes [109,110]. Some of the risks of consuming ClO2 and its derivatives are listed in Figure 45. Chlorine dioxide can be rapidly absorbed through the gastrointestinal tract. Peak blood concentration levels can be reached within 1 h after a single dose administered orally. It can also be absorbed slowly through shaved skin with a median absorption time of 22 h. Intact chlorine dioxide is unlikely to be absorbed by inhalation given its highly reactive nature; it is more likely that its derivatives can be absorbed. Chlorine dioxide is metabolized to chlorite, chlorate, and mainly chloride. Most of the administered chlorine dioxide and its metabolites remain in the plasma, followed by the kidneys, lungs, stomach, intestine, liver, and spleen. About 43% of orally administered chlorine dioxide is excreted in the urine and feces within 72 h.
It is important to note that neither chlorine dioxide nor its derivatives have undergone any evaluation or authorization by the competent authorities to ensure that the benefit/risk ratio is positive for the population.
There is no published scientific evidence that has positively considered the use of chlorine dioxide or its derivatives as a preventive or therapeutic agent against COVID-19 administered by inhalation, oral, or parenteral routes [109,110]. Some of the risks of consuming ClO 2 and its derivatives are listed in Figure 45.
ach, intestine, liver, and spleen. About 43% of orally administered chlorine dioxide is excreted in the urine and feces within 72 h.
It is important to note that neither chlorine dioxide nor its derivatives have undergone any evaluation or authorization by the competent authorities to ensure that the benefit/risk ratio is positive for the population.
There is no published scientific evidence that has positively considered the use of chlorine dioxide or its derivatives as a preventive or therapeutic agent against COVID-19 administered by inhalation, oral, or parenteral routes [109,110]. Some of the risks of consuming ClO2 and its derivatives are listed in Figure 45.  The median oral lethal dose (LD50) has been estimated to be 94 mg/kg body weight and it is therefore considered a moderately toxic and hazardous substance. The Spanish Agency for Medicines and Health Products (AEMPS) warns of serious health risks from the consumption of chlorine dioxide [111].

Antimicrobial Activity of ClO 2
Chlorine dioxide acts as an oxidizing biocide and controls the growth of Gram-positive and Gram-negative bacteria by inhibiting the transport of nutrients through the cell wall by destroying it [112]. Its effectiveness is similar or even superior in some respects to that of other known oxidants such as ozone or chlorine. It behaves as an oxidizing agent through electronic exchange, which allows it to oxidize any type of organic compound, from viruses and bacteria to proteins, hence its frequent use to purify water or certain surfaces. Pereira et al., 2008, compared the efficacy of HOCl, ClO 2 , and O 3 in the inactivation of Cryptosporidium oocyst in a public water supply from Brazilian South conditions. Experiments were carried out in samples containing 2 × 10 4 oocysts/mL of C. parvum purified from feces of experimentally contaminated calves. By using HOCl, the maximum inactivation rate obtained was 49.04% after 120 min, at 2 ppm. ClO 2 at 5 ppm inactivated 90.56% of oocysts after 90 min of contact. O 3 was the most effective product, rendering an inactivation of 100% at 24 ppm.
In the case of enveloped viruses, chlorine dioxide reacts directly with amino acid residues of proteins located on the enveloped viral surface; in the case of non-enveloped viruses, ClO 2 acts on the viral genome, affecting the ribonucleic acid RNA in the cell. By this mechanism, chlorine dioxide prevents the production of proteins and, therefore, promotes the elimination of the virus. Chlorine dioxide is a strong oxidizing agent that can be applied both in solution and in a gaseous state. It has bactericidal, fungicidal, and virucidal properties. Several food-related microorganisms, including Gram-negative and Gram-positive bacteria, yeasts and mold spores, and Bacillus cereus spores, were tested for susceptibility to 0.08 mg/L gaseous ClO 2 for 1 min at 90% relative humidity [17]. In this screening, according to Vandekinderen et al., 2009, the resistance of the different groups of microorganisms to gaseous ClO 2 generally increased in the order of Gram-negative bacteria, Gram-positive bacteria, yeast spores, molds, and Bacillus cereus spores. Factors influencing the antimicrobial efficacy of gaseous ClO 2 were its concentration, contact time, relative humidity, and temperature. Yeasts were more resistant to ClO 2 than Gram-negative and Gram-positive bacteria. Significantly, ClO 2 has been shown to be effective in inactivating Bacillus anthracis spores [113][114][115] in government and commercial buildings; however, Bacillus cereus was little affected by ClO 2 [113][114][115][116].
The resistance of different groups of microorganisms to gaseous ClO 2 generally increased in the order of Gram-negative bacteria, Gram-positive bacteria, yeast and mold spores, and Bacillus cereus spores. ClO 2 arguably provides the complete solution for disinfection because it kills the widest variety of microbes in short contact times and has fewer corrosive effects on surfaces. In addition, the use of ClO 2 avoids the threat of microbial resistance ( Figure 46). The oxidative capacity of chemicals denotes the number of electrons a molecule can accept from surrounding molecules. In the case of ClO₂, it can gain five electrons from microbial species per molecule, making it a superior biocide to alternative oxidants, which can normally only gain two. This enhanced effect is attributed to its two-step reduction ( Figure 47).  Figure 41 shows the reduction of ClO₂. In the first step, ClO₂ is reduced to chlorite after accepting one electron and then further reduced by accepting four additional electrons and four hydrogen atoms [117]. This two-step process allows it to sequester a greater number of electrons from microbes compared to other oxidants. This means that chlorine dioxide will have a reduced corrosive effect on the surfaces to which it is applied, while having a greater ability to kill. The reason why oxidizing agents such as ClO₂ are preferred to non-oxidizing disinfectants is due to their proven efficacy against bacterial spores and other microorganisms in short contact times.
Chlorine dioxide kills pathogens through electron exchange, sequestering electrons from the microorganism's structures, such as cell walls, membranes, organelles, and genetic materials, causing a molecular imbalance that leads to the death of the microorganism. Microbes cannot develop resistance to ClO₂ due to the reaction mechanism and are destroyed.
Biocides, such as quaternary ammonium compounds and triamines, contribute to increased microbial resistance, and several resistant strains, such as E. coli and C. difficile spores, have been identified. In contrast, microbial resistance is not possible with ClO₂ because of its mode of action, which is modifying microbial structures and targeting their physiological molecular integrity. This induces membrane rupture, disrupting protein function, inhibiting RNA synthesis, and killing the microbes. The oxidative capacity of chemicals denotes the number of electrons a molecule can accept from surrounding molecules. In the case of ClO 2 , it can gain five electrons from microbial species per molecule, making it a superior biocide to alternative oxidants, which can normally only gain two. This enhanced effect is attributed to its two-step reduction ( Figure 47). The oxidative capacity of chemicals denotes the number of electrons a molecule can accept from surrounding molecules. In the case of ClO₂, it can gain five electrons from microbial species per molecule, making it a superior biocide to alternative oxidants, which can normally only gain two. This enhanced effect is attributed to its two-step reduction ( Figure 47).  Figure 41 shows the reduction of ClO₂. In the first step, ClO₂ is reduced to chlorite after accepting one electron and then further reduced by accepting four additional electrons and four hydrogen atoms [117]. This two-step process allows it to sequester a greater number of electrons from microbes compared to other oxidants. This means that chlorine dioxide will have a reduced corrosive effect on the surfaces to which it is applied, while having a greater ability to kill. The reason why oxidizing agents such as ClO₂ are preferred to non-oxidizing disinfectants is due to their proven efficacy against bacterial spores and other microorganisms in short contact times.
Chlorine dioxide kills pathogens through electron exchange, sequestering electrons from the microorganism's structures, such as cell walls, membranes, organelles, and genetic materials, causing a molecular imbalance that leads to the death of the microorganism. Microbes cannot develop resistance to ClO₂ due to the reaction mechanism and are destroyed.
Biocides, such as quaternary ammonium compounds and triamines, contribute to increased microbial resistance, and several resistant strains, such as E. coli and C. difficile spores, have been identified. In contrast, microbial resistance is not possible with ClO₂ because of its mode of action, which is modifying microbial structures and targeting their physiological molecular integrity. This induces membrane rupture, disrupting protein function, inhibiting RNA synthesis, and killing the microbes.  Figure 41 shows the reduction of ClO 2 . In the first step, ClO 2 is reduced to chlorite after accepting one electron and then further reduced by accepting four additional electrons and four hydrogen atoms [117]. This two-step process allows it to sequester a greater number of electrons from microbes compared to other oxidants. This means that chlorine dioxide will have a reduced corrosive effect on the surfaces to which it is applied, while having a greater ability to kill. The reason why oxidizing agents such as ClO 2 are preferred to non-oxidizing disinfectants is due to their proven efficacy against bacterial spores and other microorganisms in short contact times.
Chlorine dioxide kills pathogens through electron exchange, sequestering electrons from the microorganism's structures, such as cell walls, membranes, organelles, and genetic materials, causing a molecular imbalance that leads to the death of the microorganism. Microbes cannot develop resistance to ClO 2 due to the reaction mechanism and are destroyed.
Biocides, such as quaternary ammonium compounds and triamines, contribute to increased microbial resistance, and several resistant strains, such as E. coli and C. difficile spores, have been identified. In contrast, microbial resistance is not possible with ClO 2 because of its mode of action, which is modifying microbial structures and targeting their physiological molecular integrity. This induces membrane rupture, disrupting protein function, inhibiting RNA synthesis, and killing the microbes.

Conclusions
In this study, the research has focused on two complementary aspects: (i) on analyzing the reactivity of ClO 2 and its possible reactions with organic and inorganic compounds; and (ii) its potential uses and its toxicity if consumed out of specification.
ClO 2 is added to drinking water to protect people from harmful bacteria and other microorganisms. The Environmental Protection Agency (EPA) recognizes chlorine dioxide use as a drinking water disinfectant, and it is included in WHO's Guidelines for drinkingwater quality. When added to drinking water, it helps destroy bacteria, viruses, and some types of parasites that can make people sick, such as Cryptosporidium parvum and Giardia lamblia. EPA regulates the maximum concentration of chlorine dioxide in drinking water to be no greater than 0.8 ppm. In medical settings, ClO 2 can be used to help sterilize equipment, surfaces, rooms, and tools. In hospitals and other healthcare environments, ClO 2 helps to sterilize medical and laboratory equipment, surfaces, rooms, and tools. Researchers have found that at appropriate concentrations, ClO 2 is both safe and effective at helping to eliminate Legionella bacteria in hospital environments. Legionella pneumophila bacteria can cause Legionnaires' disease, a potentially deadly type of pneumonia [118,119]. ClO 2 is highly reactive, reacting to oxidize inorganic and organic compounds found in water, including humic and fulvic acids, forming oxidized organic compounds such as aldehydes and carboxylic acids. Inside cells, ClO 2 oxidizes phenolic compounds, amines, amino acids, peptides, and proteins, as well as NADH, whose key function is to regulate electron and proton exchange and energy production in all cells. Their effect on biomolecules arises from interference with redox processes, modifying the electronic exchanges that occur in complexes I-IV of mitochondrial respiration and cell membranes.
Depending on concentration and frequency, it is toxic to human health, hence there are limits to its exposure to ensure safe use. The mean oral lethal dose LD50 for rats is 94 mg per kg body weight; it is therefore classified as a moderately toxic and hazardous substance. According to the classification provided by companies to the European Chemical Agency (ECHA) in the REACH registrations, this substance is fatal by inhalation, toxic by ingestion, causes severe skin burns and eye damage, and is very toxic to the environment and aquatic life, with long-lasting effects.
During the COVID-19 pandemic, the consumption of ClO 2 solutions has been promoted by non-scientists and non-medical people through different avenues (social networks, websites, mass media) for the treatment or prevention of SARS-CoV-2 infection. To date, there is no scientific evidence to uphold the use of ClO 2 or chlorine derivatives as preventive or therapeutic agents against COVID-19. Its action is unproven, and deaths have been reported, so health agencies such as the US Food and Drug Administration (FDA) have officially stated that they do not recommend taking it. Some of the common symptoms of intoxication include severe vomiting and diarrhea, anemia, severe liver failure, low blood pressure, arrythmia, and methemoglobinemia [120].
Ingestion of ClO 2 outside the regulations approved by health authorities can have serious results, including intestinal perforation. It is important to emphasize the need to follow communications and warnings from health authorities and governmental institutions. There are documented cases, both in the scientific literature and in the popular media, of severe side effects caused by ClO 2 poisoning. According to court documents, in the US alone, poison control centers have treated more than 16,000 cases of chlorine dioxide poisoning from 2014 to the end of 2020 [121]. Funding: This research was funded by project APOGEO (Cooperation Program INTERREG-MAC 2014-2020, with European Funds for Regional Development-FEDER. "Agencia Canaria de Investigación, Innovación y Sociedad de la Información (ACIISI) del Gobierno de Canarias", project ProID2020010134, Caja Canarias, project 2019SP43 and Spanish Ministry of Economy and Competitiveness (Grant PID2019-105838RB-C31).