Enhancement of trace organic contaminant degradation by crude enzyme extract from Trametes versicolor culture: Effect of mediator type and concentration
Introduction
The occurrence of trace organic contaminants (TrOCs) such as pharmaceuticals and personal care products, pesticides, steroid hormones and industrial chemicals in water and wastewater is of increasing concern. Many TrOCs have been implicated in endocrine disrupting effects on aquatic organisms and even humans, while others have been linked to ecological perturbations through acute and chronic toxicity on aquatic flora and fauna [1]. Due to the incomplete TrOC degradation in wastewater treatment plants (WWTP), WWTP effluent is a major point source of TrOC pollution. The resistance of certain TrOCs to degradation by conventional wastewater treatment has prompted research on TrOC degradation by white-rot fungi [2].
White-rot fungi can efficiently degrade a wide range of organic compounds, including many that are resistant to bacterial degradation, via one or more extracellular enzymes including lignin peroxidases, manganese-dependent peroxidases and laccase. In addition to whole-cell preparations, removal of TrOCs has been investigated either by employing crude culture extract (‘crude enzyme’) or by purified enzymes [2], [3]. Laccases are multi-copper containing enzymes that catalyze the oxidation of a wide range of phenolic substrates using oxygen as an electron acceptor [2]. The oxidation of a substrate typically involves the formation of a free radical after the transfer of a single electron to laccase. The oxidative efficiency of laccases depends on the redox potential difference between the reducing substrate and type 1 copper in laccase. Given the range of redox potentials that laccases from different fungi possess (0.17–0.80 V), non-phenolic substrates are often not amenable to direct oxidation by laccase [4], [5]. To overcome this limitation, the use of ‘redox mediators’ has been proposed.
Mediators are small molecular weight compounds that are easily oxidized by laccase. The presence of mediators can expand the catalytic activity of laccase by increasing the redox potential of the enzyme solution. Mediators also act as an “electron shuttle,” facilitating the oxidation of complex substrates that do not enter the active sites of the enzyme due to steric hindrances. Laccase oxidizes the mediators, generating highly reactive radicals, which then oxidize the target substrates [6], [7]. Three major mechanisms by which a mediator can oxidize a substrate have been reported in the literature, namely by hydrogen atom transfer (HAT), electron transfer and ionic mechanisms [6], [8]. Commonly used mediators following the HAT pathway include small molecular weight phenolic compounds and compounds containing the structural group NOH. The oxidation of these mediators by laccase generates highly reactive phenoxyl (C6H5O*) and aminoxyl (NO*) radicals, owing to the enzymatic removal of an electron followed by release of a proton [9]. These radicals then extract a hydrogen atom from the substrate. With a few exceptions (e.g. [3], [10], [11], [12]), studies on the efficacy of these mediators to remove compounds resistant to conventional treatment has to date focused mostly on compounds other than TrOCs. Furthermore, a few studies have raised concern about the toxicity of the media following treatment by laccase-mediator systems [13], [14], [15]. However, there appears to be no study which has compared the performance of redox mediators in terms of enhancement of enzymatic degradation of a diverse set of TrOCs and the resulting toxicity of the treated solution. Such a study would help identify the type and dose of mediators that improve TrOC removal while minimizing toxicity of the treated media.
The aim of this study was to investigate the performance of an extracellular enzyme extract from Trametes versicolor (ATCC 7731) culture on the removal of a set of 30 TrOCs representing diverse chemical structures (e.g., phenolic and non-phenolic moieties and electron donating/withdrawing functional groups). A special focus was given to the effect of augmenting enzymatic transformation with different dosages of two redox mediators, namely 1-hydroxybenzotriazole (HBT) and syringaldehyde (SA) on the removal performance and ultimate media toxicity. The study provides unique insights in light of the redox potential of the enzyme-mediator cocktail, the balance between the stability and reactivity of the radicals generated and their cytotoxic effects.
Section snippets
TrOC and mediators
A set of 30 TrOCs, including 11 pharmaceuticals, six pesticides, five steroid hormones, three industrial chemicals, two phytoestrogens, and three UV filters was used in this study. Key properties of these compounds are listed in Supplementary Data Table S1. These TrOCs were selected in view of their widespread occurrence in wastewater and wastewater-impacted water bodies and represent different molecular properties such as phenolic vs. non-phenolic moieties and electron donating vs. withdrawing
Degradation of TrOC by crude enzyme
The oxidation of a substrate by laccase typically involves the formation of a free radical after the transfer of a single electron to laccase. It is well known that laccase efficiently promotes single electron oxidation of phenols i.e., compounds with hydroxyl groups linked to benzene ring [2]. For example, a major role of laccase in the course of lignin degradation is the oxidation of hydroxyl groups linked to the benzene ring to form phenoxyl radicals. Further rearrangement of phenoxyl
Conclusion
This study reveals the dosage-specific comparative enhancement of enzymatic degradation of a set of 30 trace organic contaminants by two redox-mediators, namely 1-hydroxybenzotriazole (HBT) and syringaldehyde (SA). Crude enzyme extract (predominantly laccase) from T. versicolor efficiently (70–95%) degraded nine phenolic and one non-phenolic TrOCs. HBT and SA, which produce aminoxyl and phenoxyl radicals, respectively, achieved significant removal of additional five phenolic and two
Acknowledgements
A PhD scholarship to Luong N. Nguyen from the University of Wollongong is greatly appreciated. We thank Kalinda Watson for assistance with the toxicity assay.
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