22 research outputs found

    Degradation of Bunker C Fuel Oil by White-Rot Fungi in Sawdust Cultures Suggests Potential Applications in Bioremediation

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    <div><p>Fungal lignocellulolytic enzymes are promising agents for oxidizing pollutants. This study investigated degradation of Number 6 “Bunker C” fuel oil compounds by the white-rot fungi <i>Irpex lacteus</i>, <i>Trichaptum biforme</i>, <i>Phlebia radiata</i>, <i>Trametes versicolor</i>, and <i>Pleurotus ostreatus</i> (Basidiomycota, Agaricomycetes). Averaging across all studied species, 98.1%, 48.6%, and 76.4% of the initial Bunker C C10 alkane, C14 alkane, and phenanthrene, respectively were degraded after 180 days of fungal growth on pine media. This study also investigated whether Bunker C oil induces changes in gene expression in the white-rot fungus <i>Punctularia strigosozonata</i>, for which a complete reference genome is available. After 20 days of growth, a monokaryon <i>P</i>. <i>strigosozonata</i> strain degraded 99% of the initial C10 alkane in both pine and aspen media but did not affect the amounts of the C14 alkane or phenanthrene. Differential gene expression analysis identified 119 genes with ≄ log<sub>2</sub>(2-fold) greater expression in one or more treatment comparisons. Six genes were significantly upregulated in media containing oil; these genes included three enzymes with potential roles in xenobiotic biotransformation. Carbohydrate metabolism genes showing differential expression significantly accumulated transcripts on aspen vs. pine substrates, perhaps reflecting white-rot adaptations to growth on hardwood substrates. The mechanisms by which <i>P</i>. <i>strigosozonata</i> may degrade complex oil compounds remain obscure, but degradation results of the 180-day cultures suggest that diverse white-rot fungi have promise for bioremediation of petroleum fuels.</p></div

    <i>Punctularia strigosozonata</i> transcripts with predicted protein functions expressed ≄ log<sub>2</sub>(2-fold) (adjusted p < 0.01) in comparisons of 20-day growth on aspen and pine media with and without Bunker C oil.

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    <p>Positive log<sub>2</sub> fold changes indicate transcript accumulation in the first treatment while negative log<sub>2</sub> fold changes indicate transcript accumulation in the second treatment.</p><p><i>Punctularia strigosozonata</i> transcripts with predicted protein functions expressed ≄ log<sub>2</sub>(2-fold) (adjusted p < 0.01) in comparisons of 20-day growth on aspen and pine media with and without Bunker C oil.</p

    Degradation (%) of phenanthrene, a C14 alkane, and a C10 alkane in Bunker C oil by white-rot fungi.

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    <p>Degradation percentages were calculated using <a href="http://www.plosone.org/article/info:doi/10.1371/journal.pone.0130381#pone.0130381.e001" target="_blank">Eq 1</a>.</p><p>Degradation (%) of phenanthrene, a C14 alkane, and a C10 alkane in Bunker C oil by white-rot fungi.</p

    Hydrocarbon degradation by <i>Trichaptum biforme</i>.

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    <p>GC-MS chromatograms of (a) alkane and (b) phenanthrene degradation by <i>T</i>. <i>biforme</i> measured after 180 days of growth in pine media with Bunker C oil. Black lines = <i>T</i>. <i>biforme</i> profiles; blue lines = Bunker C oil profiles.</p

    MOESM1 of Genome-wide analysis of cytochrome P450s of Trichoderma spp.: annotation and evolutionary relationships

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    Additional file 1. Table S1: List of Cyp protein entries with incomplete cytochrome P450 domain. Table S2: Cytochrome P450s associated with predicted secondary metabolism-related gene clusters

    MOESM1 of The transcription factor PDR-1 is a multi-functional regulator and key component of pectin deconstruction and catabolism in Neurospora crassa

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    Additional file 1: Figure S1. Schematic depiction of phylogeny and conserved domains/signals in the pdr-1 gene and its orthologs. The amino acid sequence of N. crassa PDR-1 (NCU09033), A. niger RhaR (An13g00910), A. nidulans RhaR (AN5673) and P. stipitis TRC1 (ABN68604) was used in a conserved domain search, as well as NLS and NES prediction. The phylogeny of these proteins was determined. B. cinerea GaaR (Bcin09g00170) constitutes the outgroup in the phylogenetic tree. GAL4 = GAL4-like Zn(II)2Cys6 (or C6 zinc) binuclear cluster DNA-binding domain, fungal TF MHR = fungal transcription factor regulatory middle homology region, green triangle = nuclear localization signal, red triangle = nuclear export signal. Figure S2. Growth phenotypes and protein secretion of N. crassa WT, Δpdr-1 and pdr-1-comp strains. (A) Observed growth phenotypes. Strains were grown on either 2 mM l-Rha, 2 mM d-Xyl, 1% pectin or 1% xylan. The cultures were incubated for 3 days. (B) Sucrose pregrown cultures were switched to pectin medium and the concentration of secreted protein was determined. Error bars represent standard deviation (n = 3). Significance was determined by an independent two-sample t-test of WT against Δpdr-1 or pdr-1-comp with *p < 0.05. Figure S3. Venn diagrams of DEseq results and correlation studies of RNA-seq to RT-qPCR data. Strains were pregrown for 16 h on 2% sucrose and then switched to an induction medium of either 1% pectin (pec) or 2 mM l-Rha for an additional 4 h. (A) Differential expression analysis (DEseq) was performed on the RNA-seq data. Genes of the WT and the Δpdr-1 strains that were threefold upregulated (left diagram; +) or downregulated (right diagram; −) were compared. Venn diagrams were created with: http://bioinformatics.psb.ugent.be/webtools/Venn/ . WT on 1% pectin was used in biological duplicates; all other conditions were used in biological triplicates for the RNA-seq analysis. (B) Correlation analysis of RT-qPCR data to RNA-seq data. Axes are log10-scaled. The fold change expression of several key pectinase genes was determined by RT-qPCR in the WT and Δpdr-1 strain grown on 1% pectin and plotted against their respective RNA-seq data. The Pearson’s correlation coefficient (ρ) was determined. Two biological replicates were used for RT-qPCR except for ply-2, where only one was used. All biological replicates were analyzed as three technical replicates. Figure S4. Expression levels of pdr-1, gh28-1 and NCU09034 determined by RT-qPCR. (A) The strains were grown for 2 days on 1% pectin and the expression level of pdr-1 in the pdr-1-oex strain or gh28-1 in the gh28-1-oex and gh28-1-comp strain was determined. The WT strain was used as reference. (B) The WT and pdr-1-oex strain were incubated for 48 h on 1% xylan. 2 mM l-Rha was added and the strains were incubated for an additional 30 min before harvesting the RNA for RT-qPCR. Strains incubated for the same time but without l-Rha were used as controls. The expression of pdr-1 and NCU09034 was determined for both strains. Three biological replicates were used, except for pdr-1 in WT on pectin and NCU09034 in WT on xylan plus l-Rha, where only two were used. All biological replicates were analyzed as three technical replicates. Error bars represent standard deviation. Significance was determined by an independent two-sample t-test with **p < 0.01, ***p < 0.001. Figure S5. Expression profile of pdr-1 and biomass accumulation of the pdr-1-oex strain. (A) Expression profile of pdr-1. After a 16 h pre-incubation on 2% sucrose, biomass of the WT strain was washed three times with 1× Vogel’s solution and transferred to a medium of either no carbon source (NoC), 2% sucrose, 2 mM l-Rha or 1% pectin. The strain was incubated for an additional 4 h. Error bars represent standard deviation (n = 2 for 1% pectin, n = 3 for NoC, 2% sucrose and 2 mM l-Rha). (B) Determination of accumulated biomass. Strains were grown on 1% xylan with 0.5 mM l-Rha or d-GalA. A medium containing 1% xylan was used as control. Biomass was determined by dry weight. Error bars represent standard deviation (n = 3)
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