Allan Ian J, Semple Kirk T, Hare Rina, Reid Brian J
School of Environmental Sciences, University of East Anglia, NR4 7TJ Anglia, United Kingdom.
Environ Sci Technol. 2007 Aug 1;41(15):5498-504. doi: 10.1021/es0704939.
This work aimed to evaluate the relative contribution of soil catabolic activity, contaminant bioaccessibility, and nutrient levels on the biodegradation of field-aged polycyclic aromatic hydrocarbons and phenolic compounds in three municipal gas plant site soils. Extents of biodegradation achieved, in 6 week-long soil slurry assays, under the following conditions were compared: (i) with inoculation of catabolically active PAH and phenol-degrading microorganisms, (ii) with and without hydroxypropyl-beta-cyclodextrin supplementation (HPCD; 100 g L(-1)), and finally (iii) with the provision of additional inorganic nutrients in combination with HPCD. Results indicated no significant (p < 0.05) differences between biodegradation endpoints attained in treatments inoculated with catabolically active microorganisms as compared with the uninoculated control. Amendments with HPCD significantly (p < 0.05) lowered biodegradation endpoints for most PAHs and phenolic compounds. Only in one soil did the combination of HPCD and nutrients consistently achieve better bioremediation endpoints with respect to the HPCD-only treatments. Thus, for most compounds, biodegradation was not limited by the catabolic activity of the indigenous microorganisms but rather by processes resulting in limited availability of contaminants to degraders. It is therefore suggested that the bioremediation of PAH and phenol impacted soils could be enhanced through HPCD amendments. In addition, the biodegradability of in situ and spiked (deuterated analogues) PAHs following 120 days aging of the soils suggested that this contact time was not sufficient to obtain similar partitions to that observed for field-aged contaminants; with the spiked compounds being significantly (p < 0.05) more available for biodegradation.
这项工作旨在评估土壤分解代谢活性、污染物生物可及性和养分水平对三个城市煤气厂场地土壤中田间老化多环芳烃和酚类化合物生物降解的相对贡献。比较了在以下条件下进行的为期6周的土壤泥浆试验中实现的生物降解程度:(i)接种具有分解代谢活性的多环芳烃和酚类降解微生物;(ii)添加和不添加羟丙基-β-环糊精(HPCD;100 g L(-1));最后(iii)在添加HPCD的同时提供额外的无机养分。结果表明,与未接种的对照相比,接种具有分解代谢活性微生物的处理所达到的生物降解终点之间没有显著差异(p < 0.05)。HPCD的添加显著(p < 0.05)降低了大多数多环芳烃和酚类化合物的生物降解终点。仅在一种土壤中,HPCD和养分的组合相对于仅使用HPCD的处理始终能实现更好的生物修复终点。因此,对于大多数化合物来说,生物降解不受本地微生物分解代谢活性的限制,而是受导致降解剂可利用污染物有限的过程的限制。因此,建议通过HPCD改良来增强受多环芳烃和酚影响土壤的生物修复。此外,土壤老化120天后原位和加标(氘代类似物)多环芳烃的生物降解性表明,这段接触时间不足以获得与田间老化污染物相似的分配情况;加标化合物的生物降解可用性显著更高(p < 0.05)。