Surfactants double the biodegradation rate of persistent polycyclic aromatic hydrocarbons (PAHs) by a white-rot fungus Phanerochaete sordida

Polycyclic aromatic hydrocarbons (PAHs) are persistent in the environment and are toxic to humans and animals, rendering its remediation necessary but challenging. A white-rot fungus excellent in lignin degradation, Phanerochaete sordida YK-624, was chosen to improve biodegradation of high molecular...

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Veröffentlicht in:Environmental earth sciences 2023-06, Vol.82 (12), p.285-285, Article 285
Hauptverfasser: Li, Qiaoyu, Wang, Jianqiao, Wang, Ziyu, Zhang, Wenquan, Zhan, Hongjie, Xiao, Tangfu, Yu, Xiaolong, Zheng, Yan
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container_issue 12
container_start_page 285
container_title Environmental earth sciences
container_volume 82
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Wang, Jianqiao
Wang, Ziyu
Zhang, Wenquan
Zhan, Hongjie
Xiao, Tangfu
Yu, Xiaolong
Zheng, Yan
description Polycyclic aromatic hydrocarbons (PAHs) are persistent in the environment and are toxic to humans and animals, rendering its remediation necessary but challenging. A white-rot fungus excellent in lignin degradation, Phanerochaete sordida YK-624, was chosen to improve biodegradation of high molecular weight thus persistent PAHs, assisted by surfactants. Efficacy to degrade three PAHs, phenanthrene, pyrene and benzo(a)pyrene, representing 3-, 4-, and 5-ring structure, was compared in liquid culture at low (5 mg L −1 ) and high (50 mg L −1 ) concentrations with or without fungi and/or surfactants. At the low concentration, phenanthrene and pyrene were completely degraded by P. sordida YK-624 after 8 and 16 day incubation, while 88.9% benzo(a)pyrene degradation was observed by 24 days. Degradation of phenanthrene, pyrene and benzo(a)pyrene at the high concentration reached 89.2%, 61.9% and 28.6%, respectively, after 32 day incubation. In addition, the t 1/2 of phenanthrene were 1.17 or 11.55 days, while the t 1/2 of pyrene and benzo(a)pyrene were 1.93 or 17.33 days and 7.70 or 69.30 days, for low or high concentrations, respectively. The highest mycelial biomass at 46.1 mg was observed in incubation of 5 mg L −1 benzo(a)pyrene, exceeding the biomass in the control by 10 mg, suggesting that P. sordida YK-624 might utilize PAHs as a substrate for growth. With increasing concentration of cytochrome P450s inhibitor piperonyl butoxide (PB), the degradation of PAHs decreased, demonstrating the involvement of cytochrome P450s. For instance, the removals of phenanthrene, pyrene and benzo(a)pyrene at the low concentration were 85.7%, 36.3% and 49.0% in the presence of 500 mg L −1  PB at 24 days, compared with the controls of 100%, 100%, and 88.9%, respectively. Furthermore, three nonionic surfactants enhanced benzo(a)pyrene degradation. The 32 day degradation of benzo(a)pyrene was increased to 62.4%, 41.9% and 53.3% when 1 g L −1 Brij 30, 1 g L −1 Triton X-100, and 2 g L −1 Tween 80 were added. Benzo(a)pyrene degradation was increased approximately twofold by the addition of 1 g L −1 Brij 30. Thus, P. sordida YK-624 holds the potential for bioremediation of persistent PAHs, especially with the addition of nonionic surfactants.
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A white-rot fungus excellent in lignin degradation, Phanerochaete sordida YK-624, was chosen to improve biodegradation of high molecular weight thus persistent PAHs, assisted by surfactants. Efficacy to degrade three PAHs, phenanthrene, pyrene and benzo(a)pyrene, representing 3-, 4-, and 5-ring structure, was compared in liquid culture at low (5 mg L −1 ) and high (50 mg L −1 ) concentrations with or without fungi and/or surfactants. At the low concentration, phenanthrene and pyrene were completely degraded by P. sordida YK-624 after 8 and 16 day incubation, while 88.9% benzo(a)pyrene degradation was observed by 24 days. Degradation of phenanthrene, pyrene and benzo(a)pyrene at the high concentration reached 89.2%, 61.9% and 28.6%, respectively, after 32 day incubation. In addition, the t 1/2 of phenanthrene were 1.17 or 11.55 days, while the t 1/2 of pyrene and benzo(a)pyrene were 1.93 or 17.33 days and 7.70 or 69.30 days, for low or high concentrations, respectively. The highest mycelial biomass at 46.1 mg was observed in incubation of 5 mg L −1 benzo(a)pyrene, exceeding the biomass in the control by 10 mg, suggesting that P. sordida YK-624 might utilize PAHs as a substrate for growth. With increasing concentration of cytochrome P450s inhibitor piperonyl butoxide (PB), the degradation of PAHs decreased, demonstrating the involvement of cytochrome P450s. For instance, the removals of phenanthrene, pyrene and benzo(a)pyrene at the low concentration were 85.7%, 36.3% and 49.0% in the presence of 500 mg L −1  PB at 24 days, compared with the controls of 100%, 100%, and 88.9%, respectively. Furthermore, three nonionic surfactants enhanced benzo(a)pyrene degradation. The 32 day degradation of benzo(a)pyrene was increased to 62.4%, 41.9% and 53.3% when 1 g L −1 Brij 30, 1 g L −1 Triton X-100, and 2 g L −1 Tween 80 were added. Benzo(a)pyrene degradation was increased approximately twofold by the addition of 1 g L −1 Brij 30. 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A white-rot fungus excellent in lignin degradation, Phanerochaete sordida YK-624, was chosen to improve biodegradation of high molecular weight thus persistent PAHs, assisted by surfactants. Efficacy to degrade three PAHs, phenanthrene, pyrene and benzo(a)pyrene, representing 3-, 4-, and 5-ring structure, was compared in liquid culture at low (5 mg L −1 ) and high (50 mg L −1 ) concentrations with or without fungi and/or surfactants. At the low concentration, phenanthrene and pyrene were completely degraded by P. sordida YK-624 after 8 and 16 day incubation, while 88.9% benzo(a)pyrene degradation was observed by 24 days. Degradation of phenanthrene, pyrene and benzo(a)pyrene at the high concentration reached 89.2%, 61.9% and 28.6%, respectively, after 32 day incubation. In addition, the t 1/2 of phenanthrene were 1.17 or 11.55 days, while the t 1/2 of pyrene and benzo(a)pyrene were 1.93 or 17.33 days and 7.70 or 69.30 days, for low or high concentrations, respectively. 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Thus, P. sordida YK-624 holds the potential for bioremediation of persistent PAHs, especially with the addition of nonionic surfactants.</description><subject>Aromatic compounds</subject><subject>Aromatic hydrocarbons</subject><subject>Benzo(a)pyrene</subject><subject>Biodegradation</subject><subject>Biogeosciences</subject><subject>Biomass</subject><subject>Bioremediation</subject><subject>Cytochrome</subject><subject>cytochrome P-450</subject><subject>Cytochromes</subject><subject>Earth and Environmental Science</subject><subject>Earth Sciences</subject><subject>Environmental Science and Engineering</subject><subject>Fungi</subject><subject>Geochemistry</subject><subject>Geology</subject><subject>Hydrology/Water Resources</subject><subject>lignin</subject><subject>Liquid culture</subject><subject>liquids</subject><subject>Molecular weight</subject><subject>mycelium</subject><subject>Nonionic surfactants</subject><subject>octoxynol</subject><subject>Original Article</subject><subject>Phanerochaete sordida</subject><subject>Phenanthrene</subject><subject>phenanthrenes</subject><subject>Piperonyl butoxide</subject><subject>Polycyclic aromatic hydrocarbons</subject><subject>polysorbates</subject><subject>Pyrene</subject><subject>Ring structures</subject><subject>Substrates</subject><subject>Surfactants</subject><subject>Terrestrial Pollution</subject><subject>toxicity</subject><subject>White rot</subject><subject>White rot fungi</subject><issn>1866-6280</issn><issn>1866-6299</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2023</creationdate><recordtype>article</recordtype><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><recordid>eNp9kU1rFTEUhgdRsLT9A64CbupibD5uJpllKdoKBQvqOpwkZ-5MmTu55mSQ-Q_-aKNXFFx4NucsnvflwNM0rwR_Kzg31yRk1-mWS9UK3hve2mfNmbBd13ay75__uS1_2VwSPfE6Sqied2fN909rHiAUWAqxmFY_IysjMj-liPsMEcqUFpahIEsDO2KmiQouhR3TvIUtzFNgkNOhcoGNW8wpQPZpIXb1eHNPb5jfGLBv41SwzamwYV32K7HHERas7AhYmynlOEW4aF4MMBNe_t7nzZf37z7f3rcPH-8-3N48tEFpWVoD0ciotfRGaOQqDjuBXfSh14OMgGCC2qHvlQ6ht9ZKY7pd5Nr0PkrwXp03V6feY05fV6TiDhMFnOf6U1rJKaGVsHYnVEVf_4M-pTUv9TsnrbDaKG50peSJCjkRZRzcMU8HyJsT3P105E6OXHXkfjlytobUKUQVXvaY_1b_J_UDl4CW2g</recordid><startdate>20230601</startdate><enddate>20230601</enddate><creator>Li, Qiaoyu</creator><creator>Wang, Jianqiao</creator><creator>Wang, Ziyu</creator><creator>Zhang, Wenquan</creator><creator>Zhan, Hongjie</creator><creator>Xiao, Tangfu</creator><creator>Yu, Xiaolong</creator><creator>Zheng, Yan</creator><general>Springer Berlin Heidelberg</general><general>Springer Nature B.V</general><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7ST</scope><scope>7TG</scope><scope>7UA</scope><scope>7XB</scope><scope>88I</scope><scope>8FK</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>BHPHI</scope><scope>BKSAR</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>F1W</scope><scope>GNUQQ</scope><scope>H96</scope><scope>HCIFZ</scope><scope>KL.</scope><scope>L.G</scope><scope>M2P</scope><scope>PATMY</scope><scope>PCBAR</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PYCSY</scope><scope>Q9U</scope><scope>SOI</scope><scope>7S9</scope><scope>L.6</scope></search><sort><creationdate>20230601</creationdate><title>Surfactants double the biodegradation rate of persistent polycyclic aromatic hydrocarbons (PAHs) by a white-rot fungus Phanerochaete sordida</title><author>Li, Qiaoyu ; 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A white-rot fungus excellent in lignin degradation, Phanerochaete sordida YK-624, was chosen to improve biodegradation of high molecular weight thus persistent PAHs, assisted by surfactants. Efficacy to degrade three PAHs, phenanthrene, pyrene and benzo(a)pyrene, representing 3-, 4-, and 5-ring structure, was compared in liquid culture at low (5 mg L −1 ) and high (50 mg L −1 ) concentrations with or without fungi and/or surfactants. At the low concentration, phenanthrene and pyrene were completely degraded by P. sordida YK-624 after 8 and 16 day incubation, while 88.9% benzo(a)pyrene degradation was observed by 24 days. Degradation of phenanthrene, pyrene and benzo(a)pyrene at the high concentration reached 89.2%, 61.9% and 28.6%, respectively, after 32 day incubation. In addition, the t 1/2 of phenanthrene were 1.17 or 11.55 days, while the t 1/2 of pyrene and benzo(a)pyrene were 1.93 or 17.33 days and 7.70 or 69.30 days, for low or high concentrations, respectively. The highest mycelial biomass at 46.1 mg was observed in incubation of 5 mg L −1 benzo(a)pyrene, exceeding the biomass in the control by 10 mg, suggesting that P. sordida YK-624 might utilize PAHs as a substrate for growth. With increasing concentration of cytochrome P450s inhibitor piperonyl butoxide (PB), the degradation of PAHs decreased, demonstrating the involvement of cytochrome P450s. For instance, the removals of phenanthrene, pyrene and benzo(a)pyrene at the low concentration were 85.7%, 36.3% and 49.0% in the presence of 500 mg L −1  PB at 24 days, compared with the controls of 100%, 100%, and 88.9%, respectively. Furthermore, three nonionic surfactants enhanced benzo(a)pyrene degradation. The 32 day degradation of benzo(a)pyrene was increased to 62.4%, 41.9% and 53.3% when 1 g L −1 Brij 30, 1 g L −1 Triton X-100, and 2 g L −1 Tween 80 were added. Benzo(a)pyrene degradation was increased approximately twofold by the addition of 1 g L −1 Brij 30. Thus, P. sordida YK-624 holds the potential for bioremediation of persistent PAHs, especially with the addition of nonionic surfactants.</abstract><cop>Berlin/Heidelberg</cop><pub>Springer Berlin Heidelberg</pub><doi>10.1007/s12665-023-10970-8</doi><tpages>1</tpages></addata></record>
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subjects Aromatic compounds
Aromatic hydrocarbons
Benzo(a)pyrene
Biodegradation
Biogeosciences
Biomass
Bioremediation
Cytochrome
cytochrome P-450
Cytochromes
Earth and Environmental Science
Earth Sciences
Environmental Science and Engineering
Fungi
Geochemistry
Geology
Hydrology/Water Resources
lignin
Liquid culture
liquids
Molecular weight
mycelium
Nonionic surfactants
octoxynol
Original Article
Phanerochaete sordida
Phenanthrene
phenanthrenes
Piperonyl butoxide
Polycyclic aromatic hydrocarbons
polysorbates
Pyrene
Ring structures
Substrates
Surfactants
Terrestrial Pollution
toxicity
White rot
White rot fungi
title Surfactants double the biodegradation rate of persistent polycyclic aromatic hydrocarbons (PAHs) by a white-rot fungus Phanerochaete sordida
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