Department of Microbiology, University of Warmia and Mazury in Olsztyn, 10-727 Olsztyn, Poland.
Int J Environ Res Public Health. 2019 Jul 11;16(14):2474. doi: 10.3390/ijerph16142474.
Grass has a potential in phytoremediation and was used in this study in a potted experiment, which was performed to determine the effect of polluting soil (Eutric Cambisol) with diesel oil (DO) and unleaded petroleum (P) on the diversity of soil microorganisms, activity of soil enzymes, physicochemical properties of soil, and on the resistance of to DO and P, which altogether allowed evaluating soil health. Both petroleum products were administered in doses of 0 and 7 cm kg soil d.m. Vegetation of spanned for 105 days. Grasses were harvested three times, i.e., on day 45, 75, and 105 of the experiment. The study results demonstrated a stronger toxic effect of DO than of P on the growth and development of . Diesel oil caused greater changes in soil microbiome compared to unleaded petroleum. This hypothesis was additionally confirmed by Shannon and Simpson indices computed based on operational taxonomic unit (OTU) abundance, whose values were the lowest in the DO-polluted soil. Soil pollution with DO reduced the counts of all bacterial taxa and stimulated the activity of soil enzymes, whereas soil pollution with P diminished the diversity of bacteria only at the phylum, class, order, and family levels, but significantly suppressed the enzymatic activity. More polycyclic aromatic hydrocarbons (PAHs) were degraded in the soil polluted with P compared to DO, which may be attributed to the stimulating effect of on this process, as it grew better in the soil polluted with P than in that polluted with DO.
草具有植物修复的潜力,本研究在盆栽实验中使用了草,以确定受污染土壤(Eutric Cambisol)中柴油(DO)和无铅石油(P)对土壤微生物多样性、土壤酶活性、土壤理化性质的影响,以及对 抵抗 DO 和 P 的能力,这些综合起来可以评估土壤健康状况。两种石油产品的施用量分别为 0 和 7 cm kg 土壤干重。 的植被持续了 105 天。草分三次收割,即在实验的第 45、75 和 105 天。研究结果表明,与 P 相比,DO 对 的生长和发育具有更强的毒性作用。与无铅石油相比,DO 对土壤微生物组造成了更大的变化。这一假设还通过基于操作分类单元(OTU)丰度计算的 Shannon 和 Simpson 指数得到了进一步证实,这些指数的值在 DO 污染的土壤中最低。DO 污染土壤降低了所有细菌分类群的数量并刺激了土壤酶的活性,而 P 污染土壤仅在门、纲、目和科水平上降低了细菌的多样性,但显著抑制了酶的活性。与 DO 相比,P 污染的土壤中降解了更多的多环芳烃(PAHs),这可能归因于 P 对这一过程的刺激作用,因为 P 污染的土壤中 生长得比 DO 污染的土壤更好。