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三种原生动物分离株(种、种和种)组成的混合菌群对石油的生物降解动力学

Kinetics of petroleum oil biodegradation by a consortium of three protozoan isolates ( sp., sp. and sp.).

作者信息

Kachieng'a L, Momba M N B

机构信息

Department of Environmental, Water and Earth Sciences, Faculty of Science, Tshwane University of Technology, Arcadia Campus, P/Bag X680, Pretoria 0001, South Africa.

出版信息

Biotechnol Rep (Amst). 2017 Jul 4;15:125-131. doi: 10.1016/j.btre.2017.07.001. eCollection 2017 Sep.

DOI:10.1016/j.btre.2017.07.001
PMID:28840112
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC5558425/
Abstract

Petroleum oil is a complex mixture of substances, the majority of which are hydrocarbons; the latter represent an extremely important and heterogeneous group of compounds that find their way into water resources by anthropogenic or natural ways. The majority of toxic hydrocarbon components of petroleum are biodegradable, where bioremediation using microbial species has become an integral process for the restoration of oil-polluted areas. In this study, three bioremediation processes, namely natural attenuation, nutrient supplementation by adding glucose and biostimulation by adding Tween 80, were carried out in various petroleum hydrocarbon concentrations in polluted water media using a consortium of three protozoan isolates ( sp., sp. and sp.). A first-order kinetics model was fitted to the biodegradation data to evaluate the biodegradation rate and to determine the corresponding half-life time. First-order kinetics satisfactorily described the biodegradation of the petroleum-based contaminants under abiotic conditions. The results showed an increase in the percentage removal of petroleum oil at the lower petroleum concentrations and a gradual percentage decrease in removing petroleum oil residues occurred when there was an increase in the initial concentrations of the petroleum oil: 39%, 27%, 22%, 12%, 10% for various petroleum oil concentrations of 50, 100, 150, 200, 250 mg/L, respectively. A similar trend was also observed in the glucose-supplemented culture media where the reduction was 45% and 78% for petroleum concentrations of 250 mg/L and 50 mg/L, respectively. Biodegradation of between 33 and 90% was achieved at a Tween 80 concentration of between 50 mg/L and 250 mg/L. The degradation rate constants for the natural attenuation process ranged between ≥0 to ≤0.50, ≥0 to ≤0.35, ≥0 to ≤0.25, ≥0 to ≤ 0.14 and ≥ 0 to ≤0.11 for petroleum oil concentrations varying from 50, 100, 150, 200 and 250 mg/L, respectively, during the study after 30 days. In the presence of glucose as a nutrient supplement, the degradation rate constants increased from 0 day to 0.8 day when exposed to the lowest oil concentration of 50 mg/L, while the lowest rate constants (from 0 day to 0.25 day) were observed at the highest petroleum oil concentration of 250 mg/L for the same period. Overall enhancement of the degradation rates was achieved when adding the Tween 80 surfactant compared to the first two biodegradation processes. The longest half-life was achieved after 217 days during the natural attenuation process for samples with an oil concentration of 250 mg/L and this was reduced to 85 days using the glucose-supplemented process. There was a further decrease to 45 days when Tween 80 surfactant was added during the biostimulation process. The highest efficiency of ≥20% of Tween 80 was observed between 6 and 18 days and thereafter it decreased slightly to ≤20%.

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/dbe46df26f59/gr8.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/e0da3e8df339/gr1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/a0b1c386c02f/gr2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/46d8f87eb84d/gr3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/50ae8adc63e2/gr4.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/f7f644e35b50/gr5.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/c4ce1d367f16/gr6.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/42662ffe2b8c/gr7.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/dbe46df26f59/gr8.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/e0da3e8df339/gr1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/a0b1c386c02f/gr2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/46d8f87eb84d/gr3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/50ae8adc63e2/gr4.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/f7f644e35b50/gr5.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/c4ce1d367f16/gr6.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/42662ffe2b8c/gr7.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a9c3/5558425/dbe46df26f59/gr8.jpg
摘要

石油是一种复杂的物质混合物,其中大部分是碳氢化合物;后者是一类极其重要且种类繁多的化合物,可通过人为或自然方式进入水资源。石油中大多数有毒碳氢化合物成分是可生物降解的,利用微生物物种进行生物修复已成为恢复石油污染地区不可或缺的过程。在本研究中,使用三种原生动物分离株( 种、 种和 种)的联合体,在受污染水介质中的各种石油烃浓度下进行了三种生物修复过程,即自然衰减、添加葡萄糖进行营养补充以及添加吐温80进行生物刺激。将一级动力学模型拟合到生物降解数据中,以评估生物降解速率并确定相应的半衰期。一级动力学令人满意地描述了非生物条件下石油基污染物的生物降解情况。结果表明,在较低石油浓度下,石油去除率百分比增加,而当石油初始浓度增加时,去除石油残留的百分比逐渐下降:对于50、100、150、200、250 mg/L的各种石油浓度,去除率分别为39%、27%、22%、12%、10%。在添加葡萄糖的培养基中也观察到类似趋势,其中对于250 mg/L和50 mg/L的石油浓度,去除率分别为45%和78%。在吐温80浓度为50 mg/L至250 mg/L之间时,生物降解率达到33%至90%。在研究的30天后,自然衰减过程的降解速率常数在石油浓度分别为50、100、150、200和250 mg/L时,范围为≥0至≤0.50、≥0至≤0.35、≥0至≤0.25、≥0至≤0.14和≥0至≤0.11。在添加葡萄糖作为营养补充剂的情况下,当暴露于最低油浓度50 mg/L时,降解速率常数从第0天增加到0.8天,而在同一时期,在最高石油浓度250 mg/L时观察到最低速率常数(从第0天到0.25天)。与前两种生物降解过程相比,添加吐温80表面活性剂时实现了降解速率的总体提高。在自然衰减过程中,油浓度为250 mg/L的样品在217天后达到最长半衰期,而使用添加葡萄糖的过程时,半衰期缩短至85天。在生物刺激过程中添加吐温80表面活性剂时,半衰期进一步降至45天。在6至18天之间观察到吐温80的最高效率≥20%,此后略有下降至≤20%。

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