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Natural attenuation of fluorene and pyrene in contaminated soils and assisted with hydroxypropyl-β-cyclodextrin. Effect of co-contamination

机译:污染土壤中芴和pyr的自然衰减,并辅以羟丙基-β-环糊精。共污染的影响

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摘要

The objectives of this study were to investigate the mutual effect of the PAHs fluorene and pyrene on their respective biodegradation and dissipation processes in an agricultural soil, and to determine the effect of hydroxypro-pyl-β-cydodextrin (HPBCD), used to increase the bioavailability of PAHs, on such processes. Fluorene dissipation was primarily due to abiotic processes, although a small contribution from biodegradation was also observed. Therefore, fluorene dissipation did not increase with HPBCD and its presence did not significantly alter the dehy-drogenase activity. In contrast to fluorene, pyrene dissipation depended primarily on biotic factors, with endogenous soil microorganisms capable of degrading pyrene, with large increases in dehydrogenase activity. HPBCD increased biodegradation rate of pyrene. The co-contamination of soil with both PAHs did not affect fluorene evolution, but significantly inhibited pyrene biodegradation. The different abilities of soil bacterial consortia to catab-olize these PAHs are discussed. Additionally, the possibility that the abiotic loss of fluorene through volatilization had a significant effect on the microbial community biodegradation of both fluorene and pyrene is examined.
机译:这项研究的目的是调查PAHs芴和pyr对它们各自在农业土壤中的生物降解和消散过程的相互影响,并确定羟丙基-β-环糊精(HPBCD)的作用,以增加土壤中的PAHs。在此类过程中,PAHs的生物利用度。氟耗散主要归因于非生物过程,尽管也观察到了生物降解的微小贡献。因此,芴的耗散不会随HPBCD的增加而增加,其存在也不会显着改变脱氢酶的活性。与芴相反,pyr的消散主要取决于生物因素,内源性土壤微生物能够降解pyr,脱氢酶活性大大提高。 HPBCD可提高pyr的生物降解率。两种PAH共同污染土壤不会影响芴的进化,但会显着抑制pyr的生物降解。讨论了土壤细菌财团分解这些PAHs的不同能力。另外,还研究了通过挥发而导致的非生物芴损失对芴和pyr的微生物群落生物降解产生重大影响的可能性。

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