## 4 Conclusions  
Finally, the high degradative activities of the studied fungi toward hazardous pollutants were shown. Table 4 summarizes the properties which we found in the studied fungi. PAHs, oil, and anthraquinone dyes were the most accessible for fungal degradation. The studied surfactants were available for a limited number of fungi. The presence of activities of ligninolytic enzymes correlates with the ability of fungi to degrade pollutants. In addition, most of the studied fungi were able to produce emulsifying compounds, which, apparently, allows them to adapt to the conditions of pollution with hydrophobic pollutants. The revealed differences depended on the pollutant, the ecological and taxonomic accessory of the fungus, and, in some cases, the fungal strain. The results suggest that fungi with potential development for mycoremediation should be assessed for the following properties: the degradation of the wide range of pollutants without accumulation of the toxic metabolites; the production of emulsifying compounds; the production of ligninolytic enzymes (at least lacase and Mn-peroxidase), which can a necessary condition for the complete degradation of PAH. On the basis of the screening data, such as the degradation of wide range of pollutants without metabolites accumulation, active production of ligninolytic enzymes, and emulsifying compounds, the follow fungi can be chosen as promising for the development of mycoremediation technologies (Table 4): wood-inhabiting basidiomycetes _Pleurotus vestreuts_ f. Florida, _Schizophrenia commune_, _Trantes versicolor_ MUT 3403, and _Trantes versicolor_ DSM11372; the litter-decomposing basidiomycete _Stropharia rugososannulata_, and the ascomycete _Cladosporium herbarum_. The most active degraders of this compound include the representatives of the genus _Pleurotus_, _B. adusta_, _T. versicolor_ MUT3403, _T. gibbosa_, and ascomycete _G. candidium. P. ostreatus_ f. Florida and _B. adusta_ more actively removed the oyethyl chain, and _T. versicolor_ MUT3403 more actively degraded the aromatic ring. Perhaps the fungi, which actively destroyed both parts of the neonatal molecule, can be used for more perspective for following studies and practical use. The following supporting information can be downloaded at: [[https://www.mdpi.com/article/10.3390/app12042164/s1](https://www.mdpi.com/article/10.3390/app12042164/s1)]([https://www.mdpi.com/article/10.3390/app12042164/s1](https://www.mdpi.com/article/10.3390/app12042164/s1)), Table S1: List of fungi screened; Figure S1: IR-spectra neonol AF9-12: control treatment (blue line) and after _P. ostreatus_ Florida degradation (red line); Figure S2: IR-spectra neonol AF9-12: control treatment (blue line) and after _S. rugosomalulata_ degradation (red line); Figure S3: IR-spectra neonol AF9-12: control treatment (blue line) and after T. versicolor DSM degradation (red line); Figure S4: IR-spectra Isonolymphenol: control treatment (green line) and after Sch. commune degradation (1 week-blue and 2 weeks-red lines)  
Conceptualization, N.P., O.T. ; methodology, N.P., E.D., V.G. and E.S. ; validation, N.P., E.D. ; investigation, N.P., E.D., S.K., E.S., V.G., S.G., E.K. ; writing-original draft preparation, N.P. ; writing-review and editing N.P., D.S., G.C.V. and O.T. ; supervision, O.T. ; funding acquisition, O.T. All authors have read and agreed to the published version of the manuscript. This study was funded by the Russian Science Foundation (grant number 16-14-00081). A part of this work was further supported by the Helmholtz-Association of German Research Centres. Not applicable.