Iron(II) is oxidized by hydrogen peroxide to iron(III), forming a hydroxyl radical and a hydroxide ion in the process. Iron(III) is then reduced back to iron(II) by another molecule of hydrogen peroxide, forming a hydroperoxyl radical and a proton. The net effect is a disproportionation of hydrogen peroxide to create two different oxygen-radical species, with water (H+ + OH−) as a byproduct.[5]
Fe2+ + H2O2 → Fe3+ + HO• + OH−
1
Fe3+ + H2O2 → Fe2+ + HOO• + H+
2
2 H2O2 → HO• + HOO• + H2O
net reaction: 1+2
The free radicals generated by this process engage in secondary reactions. For example, the hydroxyl is a powerful, non-selective oxidant.[6] Oxidation of an organic compound by Fenton's reagent is rapid and exothermic and results in the oxidation of contaminants to primarily carbon dioxide and water.
Iron(II) sulfate is typically used as the iron catalyst. The exact mechanisms of the redox cycle are uncertain, and non-OH• oxidizing mechanisms of organic compounds have also been suggested.[citation needed] Therefore, it may be appropriate to broadly discuss Fenton chemistry rather than a specific Fenton reaction.
In the electro-Fenton process, hydrogen peroxide is produced in situ from the electrochemical reduction of oxygen.[8]
An example hydroxylation reaction involves the oxidation of barbituric acid to alloxane.[9] Another application of the reagent in organic synthesis is in coupling reactions of alkanes. As an example tert-butanol is dimerized with Fenton's reagent and sulfuric acid to 2,5-dimethyl-2,5-hexanediol.[10] Fenton's reagent is also widely used in the field of environmental science for water purification and soil remediation. Various hazardous wastewater were reported to be effectively degraded through Fenton's reagent.[11]
Effect of pH on formation of free radicals
pH affects the reaction rate due to a variety of reasons. At a low pH, complexation of Fe2+ also occurs, leading to lower availability of Fe2+ to form reactive oxidative species (OH•).[12] Lower pH also results in the scavenging of •OH by excess H+,[13] hence reducing its reaction rate. Whereas at high pH, the reaction slows down due to precipitation of Fe(OH)3, lowering the concentration of the Fe3+ species in solution.[11]Solubility of iron species is directly governed by the solution's pH. Fe3+ is about 100 times less soluble than Fe2+ in natural water at near-neutral pH, the ferric ion concentration is the limiting factor for the reaction rate. Under high pH conditions, the stability of the H2O2 is also affected, resulting in its self-decomposition.[14] Higher pH also decreased the redox potential of •OH thereby reducing its effectiveness.[15] pH plays a crucial role in the formation of free radicals and hence the reaction performance. Thus ongoing research has been done to optimize pH and amongst other parameters for greater reaction rates.[16]
Impacts of operation pH on reaction rate
Low pH
Formation of [Fe(H2O)6]2+ complex, hence reducing Fe2+ for radical generation
Scavenging of •OH by excess H+
High pH
Lower redox potential of •OH
Self-decomposition of H2O2 due to decreased stability at high pH
The Fenton reaction has different implications in biology because it involves the formation of free radicals by chemical species naturally present in the cell under in vivo conditions.[17]Transition-metal ions such as iron and copper can donate or accept free electrons via intracellular reactions and so contribute to the formation, or at the contrary to the scavenging, of free radicals. Superoxide ions and transition metals act in a synergistic way in the appearance of free radical damages.[18] Therefore, although the clinical significance is still unclear, it is one of the viable reasons to avoid iron supplementation in patients with active infections, whereas other reasons include iron-mediated infections.[19]
Conversion of benzene into phenol by using Fenton's reagent
Oxidation of barbituric acid into alloxan.
Coupling reactions of alkanes
Fenton-like reagent
Mixtures of Fe2+ and H2O2 are called Fenton reagent. If Fe2+ is replaced by Fe3+, it is called Fenton-like reagent.
Numerous transition metal ions and their complexes in their lower oxidation states (LmMn+) were found to have the oxidative features of the Fenton reagent, and, therefore, the mixtures of these metal compounds with H2O2 were named "Fenton-like" reagents.[21]
^Hemond, Harold (2015). Chemical Fate and Transport in the Environment (3rd ed.). Elsevier. p. 287. ISBN9780123982568.
^Koppenol, W. H. (1 December 1993). "The centennial of the Fenton reaction". Free Radical Biology and Medicine. 15 (6): 645–651. doi:10.1016/0891-5849(93)90168-t. PMID8138191.
^Casado, Juan; Fornaguera, Jordi; Galan, Maria I. (January 2005). "Mineralization of aromatics in water by sunlight-assisted electro-Fenton technology in a pilot reactor". Environmental Science and Technology. 39 (6): 1843–1847. Bibcode:2005EnST...39.1843C. doi:10.1021/es0498787. PMID15819245.
^Brömme, H. J.; Mörke, W.; Peschke, E. (November 2002). "Transformation of barbituric acid into alloxan by hydroxyl radicals: interaction with melatonin and with other hydroxyl radical scavengers". Journal of Pineal Research. 33 (4): 239–247. doi:10.1034/j.1600-079X.2002.02936.x. PMID12390507. S2CID30242100.
^Szpyrkowicz, Lidia; Juzzolino, Claudia; Kaul, Santosh N (1 June 2001). "A Comparative study on oxidation of disperse dyes by electrochemical process, ozone, hypochlorite and fenton reagent". Water Research. 35 (9): 2129–2136. Bibcode:2001WatRe..35.2129S. doi:10.1016/s0043-1354(00)00487-5. PMID11358291.
^Cai, Qinqing; Lee, Brandon Chuan Yee; Ong, Say Leong; Hu, Jiangyong (9 April 2021). "Application of a Multiobjective Artificial Neural Network (ANN) in Industrial Reverse Osmosis Concentrate Treatment with a Fluidized Bed Fenton Process: Performance Prediction and Process Optimization". ACS ES&T Water. 1 (4): 847–858. doi:10.1021/acsestwater.0c00192. S2CID234110033.
^Matavos-Aramyan, S.; Moussavi, M.; Matavos-Aramyan, H.; Roozkhosh, S. (2017). "Cryptosporidium-contaminated water disinfection by a novel Fenton process". Free Radical Biology and Medicine. 106: 158–167. doi:10.1016/j.freeradbiomed.2017.02.030. PMID28212822. S2CID3918519.
^Robbins; Cotran (2008). Pathologic basis of disease (7th ed.). Elsevier. p. 16. ISBN978-0-8089-2302-2.