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石油炼制厂污染土壤的中观试验:自然衰减、生物刺激和生物强化的比较。

Mesocosm trials of bioremediation of contaminated soil of a petroleum refinery: comparison of natural attenuation, biostimulation and bioaugmentation.

机构信息

CIMAR/CIIMAR - Centro Interdisciplinar de Investigação Marinha e Ambiental, Universidade do Porto, Rua dos Bragas 289, 4050-123, Porto, Portugal.

出版信息

Environ Sci Pollut Res Int. 2010 Aug;17(7):1339-46. doi: 10.1007/s11356-010-0318-y. Epub 2010 Mar 14.

DOI:10.1007/s11356-010-0318-y
PMID:20229281
Abstract

PURPOSE

Contamination with petroleum hydrocarbons (PHC) is a global problem with environmental implications. Physico-chemical treatments can be used for soil cleanup, but they are expensive, and can have implications for soil structure and environment. Otherwise, biological remediation treatments are cost-effective and restore soil structure. Several remediation experiments have been carried out in the lab and in the field; however, there is the challenge to achieve as good or better results in the field as in the laboratory. In the ambit of a project aiming at investigating suitable biological remediation approaches for recovering a refinery contaminated soil, we present here results obtained in bioremediation trials. The approaches biostimulation and bioaugmentation were tested, in parallel, and compared with natural attenuation. For this purpose, mesocosm experiments were carried out inside the refinery area, which constitutes a real asset of this work.

METHODS

Soil contaminated with crude oil was excavated, re-contaminated with turbine oil, homogenised and used to fill several 0.5 m(3) high-density polyethylene containers. The efficiency of procedures as follows: (1) natural attenuation; (2) manual aeration; (3) biostimulation by adding (3.1) only nutrients; and (3.2) nutrients and a non-ionic surfactant; and (4) bioaugmentation in the presence of added (4.1) nutrients or (4.2) nutrients and a non-ionic surfactant were evaluated after a 9-month period of experiment. For bioaugmentation, a commercial bacterial product was used. In addition to physico-chemical characterization, initial and final soil contents in total petroleum hydrocarbons (TPH) (by Fourier transform infrared spectrophotometry) and the total number of bacteria (by total cell counts) were carried out. For TPH degradation evaluation the soil was divided in four fractions corresponding to different depths: 0-5; 5-10; 10-15; and 15-20 cm. Mean values of percentages of PHC degradation varied between 20 and 50% at surface and between 10 and 35% below 5-cm depth. Natural attenuation was as efficient as most of the tested treatments (about 30% TPH degradation) being exceeded only by bioaugmentation combined with nutrient and surfactant amendments (about 50% TPH degradation). Higher TPH degradation at surface suggests that a combination of sufficient dioxygen, propitious for aerobically degradation, with sunlight required for production of strong photochemical oxidants like ozone, contributed for enhancing degradation. Indeed, the atmosphere of the refineries is relatively rich in volatile organic compounds and nitrogen dioxide (a side-product of the combustion of residual volatile PHC released by the chimneys), which are precursors of O(3) and other photochemical oxidants produced in sunny days, which are very common in Portugal. The fact that natural attenuation was as efficient as most of the soil treatments tested was very probably a result of the presence, in the initial soil, of physiologically adapted native microorganisms, which could be efficient in degrading PHC.

CONCLUSIONS

A cost-effective way to reduce half-life for the degradation of PHC of contaminated soil of the refinery will be a periodic revolving of the soil, like tillage, in order to expose to the oxidative atmosphere the different layers of contaminated soil. A combination of soil revolving with bioaugmentation together with nutrients and surfactant amendments may result in an additional improvement of PHC degradation rate. However, this last procedure will raise markedly the price of the remediation treatment.

摘要

目的

石油碳氢化合物(PHC)污染是一个具有环境影响的全球性问题。物理化学处理可用于土壤清理,但成本高昂,并且可能对土壤结构和环境产生影响。否则,生物修复处理具有成本效益,并能恢复土壤结构。已经在实验室和现场进行了多次修复实验;然而,在现场获得与实验室相同或更好的结果是具有挑战性的。在一个旨在调查适合恢复炼油厂污染土壤的生物修复方法的项目范围内,我们在此介绍了在生物修复试验中获得的结果。生物刺激和生物增强两种方法进行了测试,并与自然衰减进行了比较。为此,在炼油厂区域内进行了中尺度实验,这是这项工作的一个实际资产。

方法

挖掘出受原油污染的土壤,用涡轮机油重新污染,均质化,然后用于填充几个 0.5 立方米的高密度聚乙烯容器。以下程序的效率:(1)自然衰减;(2)手动曝气;(3)通过添加(3.1)仅营养物;和(3.2)营养物和非离子表面活性剂进行生物刺激;和(4)在添加(4.1)营养物或(4.2)营养物和非离子表面活性剂的情况下进行生物增强,在 9 个月的实验期后进行评估。对于生物增强,使用了一种商业细菌产品。除了物理化学特性外,还进行了初始和最终土壤中总石油烃(TPH)的含量(通过傅里叶变换红外分光光度法)和总细菌数(通过总细胞计数)的测定。为了评估 TPH 的降解,将土壤分为四个对应于不同深度的部分:0-5cm;5-10cm;10-15cm;和 15-20cm。TPH 降解的平均百分比在表面之间变化在 20%至 50%之间,在 5cm 以下深度之间变化在 10%至 35%之间。自然衰减与大多数测试处理一样有效(约 30%的 TPH 降解),仅被生物增强与营养物和表面活性剂添加的组合(约 50%的 TPH 降解)超过。表面处较高的 TPH 降解表明,充足的需氧降解所需的氧气与阳光的组合,对于增强降解很重要,阳光对于生产臭氧等强光化学氧化剂是必需的。事实上,炼油厂的大气中相对富含挥发性有机化合物和二氧化氮(烟囱释放的残留挥发性 PHC 燃烧的副产物),它们是 O(3)和其他在葡萄牙很常见的阳光明媚的日子里产生的光化学氧化剂的前体。自然衰减与大多数测试的土壤处理一样有效,这很可能是由于初始土壤中存在生理上适应的本地微生物,这些微生物可以有效地降解 PHC。

结论

减少炼油厂污染土壤中 PHC 半衰期的一种具有成本效益的方法将是定期旋转土壤,如耕作,以便将不同层的污染土壤暴露于氧化气氛中。土壤旋转与生物增强相结合,同时添加营养物和表面活性剂,可能会进一步提高 PHC 的降解率。然而,最后一个程序将大大提高修复处理的价格。

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