The aquatic hyphomycete
Clavariopsis aquatica was used to quantify the effects of extracellular laccase and intracellular reactions on the isomer-specific biotransformation of technical nonylphenol (t-NP). In laccase-producing cultures, maximal removal rates of t-NP and the isomer 4-(1-ethyl-1,4-dimethylpentyl)phenol (NP112) were about 1.6- and 2.4-fold higher, respectively, than in laccase-lacking cultures. The selective suppression of either laccase or intracellular reactions resulted in essentially comparable maximal removal rates for both compounds. Evidence for an unspecific oxidation of t-NP isomers was consistently obtained from laccase-expressing fungal cultures when intracellular biotransformation was suppressed and from reaction mixtures containing isolated laccase. This observation contrasts with the selective degradation of t-NP isomers by bacteria and should prevent the enrichment of highly estrogenic isomers in remaining t-NP. In contrast with laccase reactions, intracellular fungal biotransformation caused a significant shift in the isomeric composition of remaining t-NP. As a result, certain t-NP constituents related to more estrogenic isomers were less efficiently degraded than others. In contrast to bacterial degradation via
ipso-hydroxylation, the substitution pattern of the quaternary α-carbon of t-NP isomers does not seem to be very important for intracellular transformation in
C. aquatica. As-yet-unknown intracellular enzymes are obviously induced by nonylphenols. Mass spectral data of the metabolites resulting from the intracellular oxidation of t-NP, NP112, and 4-(1-ethyl-1,3-dimethylpentyl)phenol indicate nonyl chain hydroxylation, further oxidation into keto or aldehyde compounds, and the subsequent formation of carboxylic acid derivatives. Further metabolites suggest nonyl chain desaturation and methylation of carboxylic acids. The phenolic moieties of the nonylphenols remained unchanged.Nonylphenol ethoxylates (NPEOs) represent a major group of industrial nonionic surfactants. Technical nonylphenol (t-NP), used for the production of NPEOs, is synthesized by Friedel-Crafts alkylation of phenol with a mixture of differently branched nonenes. It therefore comprises a great variety of mainly
para-substituted isomers, with variously branched nonyl chains. About 50 to 80 t-NP isomers were estimated to occur in environmentally relevant matrices (
19). The incomplete bioconversion of NPEOs in wastewater treatment plants results in the formation of the less biodegradable t-NP and is considered a major source of this contaminant in the aquatic environment (
57). The recalcitrance of t-NP to biodegradation is partly due to the presence in more than 85% of the t-NP isomers of a quaternary α-carbon in the branched nonyl chain. Such structural characteristics are considered to limit biological nonyl chain oxidation (
11,
53,
55). Nonylphenols are known to disrupt normal endocrine functions in vertebrates (
57). Certain isomers contained in t-NP have been reported to possess a considerably higher estrogenic activity than the t-NP mixture (
15). Due to increasing concerns with respect to their largely unknown environmental fate and potentially adverse environmental and human health effects, nonylphenols have been listed as priority hazardous substances in the EU water framework directive.In light of the concerns above, microbial reactions with the potential to reduce nonylphenol concentrations in the environment but also offering new possibilities for applications such as effluent treatment have received increasing attention (
11). Among environmental microorganisms, both aquatic and terrestrial fungi, as well as bacteria, have been shown to degrade t-NP (
11). Fungal attack on nonylphenols differs from bacterial nonylphenol degradation. In the case of intracellular nonylphenol biotransformation reactions catalyzed by fungi, only metabolites modified in the alkyl chain have been described (
23,
52). Metabolites indicative of oxidation of the phenolic ring have not been described to date. Bacterial degradation pathways have only been documented in the genera
Sphingomonas and
Sphingobium. Bacterial mineralization of the aromatic moiety of t-NP isomers to CO
2 and H
2O is initiated via ring hydroxylation at the
ipso (C-4) position of the phenolic ring, and nonanols are produced from the nonyl chains (
10,
11,
15,
16). Bacteria have been shown to utilize branched-chain nonylphenols as growth substrates (
11,
12,
17,
43). In contrast, only one report describes the growth of a fungus, the yeast
Candida aquaetextoris, on nonylphenol (the isomer 4-
n-NP containing a linear nonyl chain) (
52). With respect to fungal attack on t-NP, cometabolism seems to be the dominating process (
11). Recent literature data indicate that certain t-NP isomers with an estrogenic potency higher than those of the original t-NP mixture can be enriched in remaining t-NP. This results from the selective removal of individual isomers upon bacterial
ipso-substitution degradation mechanisms (
15). However, the effects of fungal biotransformation reactions on the isomeric profile of t-NP have not yet been quantified.Laccases are extracellular multicopper oxidases. These have most frequently been described in white-rot basidiomycetes, which unspecifically oxidize via one-electron abstraction certain lignin constituents, as well many xenobiotic compounds. Thereby, organic radicals are generated as the primary oxidation products (
3). Among the several groups of fungi found in aquatic environments, aquatic hyphomycetes (AQH) are a phylogenetically diverse group of mitosporic fungi specifically adapted to their exclusively aquatic lifestyle. AQH have been shown to metabolize several organic environmental pollutants, including t-NP (
23), polycyclic musk fragrances (
31), pesticide metabolites (
2), and synthetic dyes (
22). Therefore, with respect to the fungal attack on organic pollutants found in aquatic ecosystems, AQH are of special importance. Laccase production by strictly aquatic fungi such as AQH has already been demonstrated and discussed in the context of lignocellulose decay in aquatic ecosystems (
1). A role of this enzyme in the AQH-catalyzed breakdown of aquatic environmental pollutants has been recently suggested. Here, laccase isolated from the AQH
Clavariopsis aquatica was shown to act on nonylphenol (
23) and polycyclic musk fragrances (
31). Laccase has also been implicated in nonylphenol degradation by white-rot fungi (
44,
45). Isolated extracellular laccases from several aquatic and terrestrial fungi were shown to catalyze the formation of oligomeric coupling products from nonylphenols via organic radical intermediates (
6,
11). However, the effects of laccase reactions on the isomeric patterns of t-NP have not been assessed to date.The aim of the present study was to quantify the influence of extracellular laccase catalysis and intracellular biotransformation on nonylphenol removal rates and on the isomeric composition of t-NP. For this,
C. aquatica was used as a model organism. The derived data were compared to effects of bacteria on nonylphenol isomers reported by other authors (
15), and environmental and biotechnological implications of fungal t-NP biotransformation were deduced. At the same time we addressed metabolite formation from t-NP and the two major t-NP isomers 4-(1-ethyl-1,3-dimethylpentyl)phenol (NP111) and 4-(1-ethyl-1,4-dimethylpentyl)phenol (NP112) (Fig. ). This was done to substantiate the apparent differences between fungi and bacteria in the intracellular oxidation of t-NP (
11,
15).
Open in a separate windowChemical structures of the nonylphenol isomers NP111 and NP112.
相似文献