Degradation of hydrocarbon components contaminated in oily waste-water collected in Doxa petroleum storage, Hanoi by microbial biofilm attached on coconut fiber
Main Article Content
Abstract
Oily waste-water is generated in many industrial processes, such as oil refining, oil storage, exploration, transportation, washing ... Oily waste water poses a great problem with water environment, ecosystem and human health. Nowadays, application of microbial biofilm for the removal of oil and derivatives from contaminated environments has received much attention. Microbial biofilms are defined as complex coherent structure of cells and cellular products, which are attached on solid surface. In biofilm structure, microorganisms increase their ability to grow and survive in changing environmental conditions and increase their access to absorb substrates or nutrients. This study focused on the degradation of hydrocarbon components contaminated in oil polluted waste water by biofilm formed by a mixture of bacterial and yeast strains isolated from oil contaminated water in Viet Nam attached on coconut fiber carriers in 2000 liter system. As the results, biofilm attached on coir carrier could degrade 62% after 5 days and 99,9% after 7 days of the total amount of oil with the initial concentration of 31.950 mg/l. Phenol and polycyclic aromatic hydrocarbons (PAHs) also were degraded up to 99.9% phenol and more than 94,8%PAHs in oily wastewater. This result gave hint to develop new method to treat petroleum oil contaminated water in Vietnam.
References
[2] Sun C, Leiknes T, Weitzenbock J &Thorstensen B. Development of a biofilm – MBR for shipboard wastewater treatment: the effect of process configuration. Desalination, 250, 2 (2010), 745-750.
[3] Pendashteh AR, Fakhru’l- Razi A, Madaeni SS, Abdullah LC, Abidin ZZ & Biak ARA. Membrane foulants characterization in a membrane bioreactor (MBR) treating hypersaline oily wastewater. Chemical Engineering Journal, 168 (2011), 140-150.
[4] O’toole GA, Kaplan H &Kolter R. Biofilm formation as microbial development. Annual Review of Microbiology, 54 (2000), 49-79.
[5] Cheng KC, Demirci A, Catchmark JM. Advances in biofilm reactors for production of value-added products. Applied Microbiology and Biotechnology, 87 (2010), 445-456.
[6] Huysman P, Meenen P, van Assche P &Vertraete W. Factors affecting the colonization of non porous and porous packing materials in model up flow methane reactor. Biotechnology Letter, 5 (1983), 643-648.
[7] Kawase M, Nomura T, Najima T. An anaerobic fixed bed reactor with a porous ceramic carrier. Water Science & Technology, 21 (1989), 77-86.
[8] Lê Thị Nhi Công, Vũ Ngọc Huy, Đỗ Văn Tuân, Đỗ Thị Liên, Hoàng Phương Hà, Đỗ Thị Tố Uyên. Đánh giá khả năng xử lý nước thải nhiễm dầu bằng màng sinh học do vi sinh vật tạo thành được gắn trên vật liệu mang xơ dừa ở các hệ thử nghiệm dung tích 300 lít/ngày. Tạp chí Công nghệ Sinh học, 14, 1A (2016), 587-593.
[9] Nhi – Cong LT, Cung TNM, Morikawa M &Nghiem NM. Transformation of iso – pentylbanzene by a biofilm – forming strain of Candida viswanathii TH1 isolated from oil – polluted sediments collected in coastal zones in Vietnam. Journal of Environmental Science and Health, Part A 49 (2014), 777-786.
[10] Krystyna P, Andrzej W & Magdalena P. The isolation of microorganisms capable of phenol degradation. Polish Journal of Microbiology, 55,1 (2006), 63-67