Andersson B Erik, Lundstedt Staffan, Tornberg Karin, Schnürer Ylva, Oberg Lars G, Mattiasson Bo
Department of Biotechnology, Center for Chemistry and Chemical Engineering, Lund University, PO. Box 124, SE-221 00 Lund, Sweden.
Environ Toxicol Chem. 2003 Jun;22(6):1238-43.
Soil artificially contaminated with fluorene, phenanthrene, pyrene, and benz[a]anthracene was inoculated with the wood-rotting fungi Plrurotus ostreatus and Antrodia vaillantii. During 12 weeks of incubation, polycyclic aromatic hydrocarbon (PAH) degradation and the formation of persistent degradation products were monitored by chemical analysis. In addition, the effect on the indigenous soil bacteria was studied by plate count techniques and by measuring the concentration of bacteria-specific phospholipid fatty acids (PLFAs). In both soils inoculated with fungi, the PAH degradation was enhanced compared to the control soil without fungi. The white-rot fungus P. ostreatus accelerated the degradation rate radically the first weeks, while the effect of the brown-rot fungus was more pronounced at later stages during the 12-week study. In a soil with no amendments, the final degradation result was similar to that in the soil with added fungi, although the degradation pattern for the individual PAHs was different. Furthermore, the degradation by P. ostreatus was accompanied by an accumulation of PAH metabolites, that is, 9-fluorenone, benz[a]anthracene-7,12-dione, and two compounds identified as 4-hydroxy-9-fluorenone and 4-oxapyrene-5-one, that was not seen in the other soils. The inoculation with the white-rot fungus also had a large negative effect on the indigenous soil bacteria. This could be an important drawback of using the white-rot fungus P. ostreatus in soil bioremediation since a sequential fungal-bacterial degradation probably is needed for a complete degradation of PAHs in soil. In the soil inoculated with A. vaillantii, on the other hand, no metabolites accumulated, and no negative effects were observed on the indigenous microorganisms.
用芴、菲、芘和苯并[a]蒽人工污染的土壤接种了木腐真菌糙皮侧耳和瓦氏多孔菌。在12周的培养过程中,通过化学分析监测多环芳烃(PAH)的降解和持久性降解产物的形成。此外,通过平板计数技术和测量细菌特异性磷脂脂肪酸(PLFA)的浓度来研究对土壤原生细菌的影响。与未接种真菌的对照土壤相比,两种接种了真菌的土壤中PAH的降解都有所增强。白腐真菌糙皮侧耳在最初几周极大地加速了降解速率,而在为期12周的研究后期,褐腐真菌的效果更为明显。在未添加改良剂的土壤中,最终降解结果与添加真菌的土壤相似,尽管单个PAH的降解模式不同。此外,糙皮侧耳的降解伴随着PAH代谢物的积累,即9-芴酮、苯并[a]蒽-7,12-二酮,以及两种被鉴定为4-羟基-9-芴酮和4-氧杂芘-5-酮的化合物,而在其他土壤中未观察到这种情况。接种白腐真菌对土壤原生细菌也有很大的负面影响。这可能是在土壤生物修复中使用白腐真菌糙皮侧耳的一个重要缺点,因为土壤中PAHs的完全降解可能需要真菌-细菌的顺序降解。另一方面,在接种了瓦氏多孔菌的土壤中,没有代谢物积累,也未观察到对原生微生物的负面影响。