Enhancing the production of hydroxyl radicals by Pleurotus eryngii via quinone redox cycling for pollutant removal.

The induction of hydroxyl radical (OH) production via quinone redox cycling in white-rot fungi was investigated to improve pollutant degradation. In particular, we examined the influence of 4-methoxybenzaldehyde (anisaldehyde), Mn(2+), and oxalate on Pleurotus eryngii OH generation. Our standard quinone redox cycling conditions combined mycelium from laccase-producing cultures with 2,6-dimethoxy-1,4-benzoquinone (DBQ) and Fe(3+)-EDTA. The main reactions involved in OH production under these conditions have been shown to be (i) DBQ reduction to hydroquinone (DBQH(2)) by cell-bound dehydrogenase activities; (ii) DBQH(2) oxidation to semiquinone (DBQ(-)) by laccase; (iii) DBQ(-) autoxidation, catalyzed by Fe(3+)-EDTA, producing superoxide (O(2)(-)) and Fe(2+)-EDTA; (iv) O(2)(-) dismutation, generating H(2)O(2); and (v) the Fenton reaction. Compared to standard quinone redox cycling conditions, OH production was increased 1.2- and 3.0-fold by the presence of anisaldehyde and Mn(2+), respectively, and 3.1-fold by substituting Fe(3+)-EDTA with Fe(3+)-oxalate. A 6.3-fold increase was obtained by combining Mn(2+) and Fe(3+)-oxalate. These increases were due to enhanced production of H(2)O(2) via anisaldehyde redox cycling and O(2)(-) reduction by Mn(2+). They were also caused by the acceleration of the DBQ redox cycle as a consequence of DBQH(2) oxidation by both Fe(3+)-oxalate and the Mn(3+) generated during O(2)(-) reduction. Finally, induction of OH production through quinone redox cycling enabled P. eryngii to oxidize phenol and the dye reactive black 5, obtaining a high correlation between the rates of OH production and pollutant oxidation.

Induction of extracellular hydroxyl radical production by white-rot fungi through quinone redox cycling.

A simple strategy for the induction of extracellular hydroxyl radical (OH) production by white-rot fungi is presented. It involves the incubation of mycelium with quinones and Fe(3+)-EDTA. Succinctly, it is based on the establishment of a quinone redox cycle catalyzed by cell-bound dehydrogenase activities and the ligninolytic enzymes (laccase and peroxidases). The semiquinone intermediate produced by the ligninolytic enzymes drives OH production by a Fenton reaction (H(2)O(2) + Fe(2+) --> OH + OH(-) + Fe(3+)). H(2)O(2) production, Fe(3+) reduction, and OH generation were initially demonstrated with two Pleurotus eryngii mycelia (one producing laccase and versatile peroxidase and the other producing just laccase) and four quinones, 1,4-benzoquinone (BQ), 2-methoxy-1,4-benzoquinone (MBQ), 2,6-dimethoxy-1,4-benzoquinone (DBQ), and 2-methyl-1,4-naphthoquinone (menadione [MD]). In all cases, OH radicals were linearly produced, with the highest rate obtained with MD, followed by DBQ, MBQ, and BQ. These rates correlated with both H(2)O(2) levels and Fe(3+) reduction rates observed with the four quinones. Between the two P. eryngii mycelia used, the best results were obtained with the one producing only laccase, showing higher OH production rates with added purified enzyme. The strategy was then validated in Bjerkandera adusta, Phanerochaete chrysosporium, Phlebia radiata, Pycnoporus cinnabarinus, and Trametes versicolor, also showing good correlation between OH production rates and the kinds and levels of the ligninolytic enzymes expressed by these fungi. We propose this strategy as a useful tool to study the effects of OH radicals on lignin and organopollutant degradation, as well as to improve the bioremediation potential of white-rot fungi.