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

机译:石油精炼厂污染土壤的生物修复的中观试验:自然衰减,生物刺激和生物强化的比较

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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 anonionic 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 30% 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 ery 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 period ic revolving of the soil, like tillage, in orderto expose to the oxidative atmosphere the different layers ofcontaminated soil. A combination of soil revolving withbioaugmentation together with nutrients and surfactantamendments may result in an additional improvement of PHC degradation rate. However, this last procedure will raise markedly the price of the remediation treatment.
机译:目的用石油碳氢化合物(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净化,但价格昂贵,可能会对土壤结构和环境产生影响。否则,生物修复处理将具有成本效益,并能恢复土壤结构。在实验室和现场已经进行了一些修复实验。然而,要在野外取得与实验室一样好的或更好的结果是一个挑战。在旨在研究合适的生物修复方法以回收精炼厂污染土壤的项目的范围内,我们在此介绍在生物修复试验中获得的结果。并行测试了生物刺激和生物强化的方法,并与自然衰减进行了比较。为此,在炼油厂区域内进行了介观试验,这是这项工作的真正资产。方法挖掘被原油污染的土壤,再用汽轮机油污染,均质,并用其填充数个0.5 m〜3高密度聚乙烯容器。程序的效率如下:(1)自然衰减; (2)人工曝气; (3)仅添加(3.1)营养素进行生物刺激; (3.2)营养物质和阴离子表面活性剂; (9)在9个月的实验后,评估了在添加(4.1)营养物或(4.2)营养物和非离子表面活性剂存在下的生物增强作用。为了生物增强,使用了商业细菌产品。除了理化特性外,还进行了总石油烃(TPH)中的初始和最终土壤含量(通过傅里叶变换红外分光光度法)和细菌总数(通过总细胞数)。为了进行TPH降解评估,将土壤分为对应于不同深度的四个部分:0-5; 0-5。 5-10; 10-15;和15–20厘米。 PHC降解百分比的平均值在表面上介于20%至50%之间,在5厘米以下深度介于10%至35%之间。自然衰减与大多数测试处理(大约30%TPH降解)仅通过生物增强结合营养和表面活性剂的补充而超过的效率一样。表面较高的TPH降解表明,有利于需氧降解的充足双氧与产生强光化学氧化剂(如臭氧)所需的阳光共同促进了降解。的确,精炼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燃烧的副产品),它们是O_3和晴天产生的其他光化学氧化剂的前体,在葡萄牙很常见。自然衰减与大多数测试土壤处理一样有效的事实,很可能是由于在初始土壤中存在生理适应性天然微生物而产生的,这可以有效降解PHC。结论减少精炼厂被污染土壤的PHC降解的半衰期的一种经济有效的方法是土壤的周期性旋转(例如耕作),以使不同层次的被污染土壤暴露于氧化性气氛。结合生物增效作用的土壤旋转以及养分和表面活性剂的改良可共同提高PHC降解率。但是,此最后步骤将明显提高补救措施的价格。

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