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Biocatalytic desulfurization of dibenzothiophene by Pseudomonas sp. strain KWN5

IDA BAGUS WAYAN GUNAM*1, I GUSTI AYU LANI TRIANI1, NYOMAN SEMADI

ANTARA1, AGUS SELAMET DUNIAJI2, YOHANES SETIYO3 AND

DEWA ADI SUPATA1

1

Bioindustry Laboratory, Department of Agro-Industrial Technology, 2Department of Food Science and Technology, 3Department of Agricultural Engineering,

Faculty of Agricultural Technology, Udayana University, Denpasar, Bali, Indonesia

ABSTRACT

Pseudomonas sp. strain KWN5 was tested for the ability to use dibenzothiophene in n -tetradecane as the sole of sulfur source. The strain could grow on mineral salt sulfur-free

(MSSF) medium with the n-tetradecane oil phase containing 200 ppm dibenzothiophene

(DBT) and desulfurize this compound. The DBT-desulfurizing ability of KWN5 is high

over a wide temperature range from 27 to 42oC, and the highest at 37oC. This strain could

grow well on incubation period for 4 days at 37oC, pH 7, and glucose as the carbon source.

In that condition, growing cells of KWN5 could degrade 200 ppm DBT around 75.21% within 96 h, indicating that this strain was very useful for the removal of DBT from oil.

Keywords: Desulfurization, dibenzothiophene, tetradecane, strain KWN5

INTRODUCTION

Production and world primary energy consumption showed a high increase. Energy demand increases with increasing income level. The energy of the most widely used today is still from fossil energy. Use of fossil energy, especially petroleum widely acknowledged having benefits but also having a negative impact.

The result of incomplete combustion of petroleum and coal produce sulfur oxides

(SOx), which can cause environmental pollution such as air pollution and acid rain (Gunam

et al., 2006). Sources of air pollution in each area are different. Sources of air pollution may come from motor vehicles, household activities, and industry (Laras 2006).

Petroleum contains sulfur compounds, including aromatic sulfur compounds such as alkyl dibenzothiophene and benzothiophene. Its compounds cannot be removed by

conventional hydrodesulfurization (HDS) treatment using metallic catalysts (Furuya et al.

2003; Gunam et al. 2006). This proves that the use of HDS require high costs, so many

researchers turned its attention to seeking a more efficient alternative technologies (Guerinik and Muttawah 2003).

One attempt to reduce the sulfur content of aromatic compounds in petroleum is biodesulfurization process. In this process, the microbes use sulfur from petroleum as an energy source for growth. To obtain optimal results in lowering the sulfur content of petroleum, required certain types of bacteria that have the ability to degrade these compounds. Efforts to reduce the sulfur content of aromatic compounds in petroleum can be optimized (Jasrizal, 2009).

Results of previous studies (Gunam et al. 2009), showed that one strain has the highest

ability to degrade aromatic sulfur compounds, known as KWN5 strain (this strain was isolated from soil samples derived from petroleum-contaminated soil near oil fields Kawengan, Bojonegoro, East Java). Based on the above, it is necessary to investigate the optimum conditions (temperature and pH) for the growth of this strain, which can degrade the highest DBT compounds

MATERIALS AND METHODS Materials

Dibenzothiophene (DBT) was purchased from Aldrich and Tetradecane was supplied by Wako Pure Chemical Co., Osaka, Japan. Mineral Salt Sulfur Free (MSSF) Medium was

prepared by previous method (Gunam et al. 2006) and petroleum (light gas oil) was

supplied by Pertamina. All other reagents were of analytical grade and commercially available.

A concentrated fraction of aromatic compounds (CA) was prepared by fractionation of

commercial light gas oil (Gunam et al. 2006).

*

Correspondence author: Phone: +62 361 222006; Fax: +62 0361 701801;

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Bacterial strains and culture media

The KWN5 strain was grown in a mineral salt sulfur-free (MSSF) medium (pH 7) with

CA as the sole sulfur source, as reported in our previous paper (Gunam et al. 2011).

MSSF-TD was the standard media for the desulfurization assay, consisted of MSSF: n-tetradecane

= 5:1, with DBT dissolved in n-tetradecane. Bacterial growth was determined by measuring

OD660 of water layer (Gunam et al. 2006).

Seed culture preparation

For seed culture production, KWN5 was cultivated at 30oC in 500-ml Erlenmeyer

flasks containing 200 ml of MSSF medium with CA as the sole source of sulfur for 4 days.

The cells were harvested by centrifugation at 3500 rpm for 20 min at 4oC, washed twice

with 0.85% saline solution and suspended in the same solution. The optical density at 660

nm (OD660) of the cell suspension was adjusted to 5.

Bio-desulfurization assay

Six milliliter of MSSF-TD medium containing DBT were inoculated with 0.1 ml of the

seed culture (OD660 = 5) and incubated at various temperature and initial pH for 4 days with

shaking (200 rpm). After incubation, the organic layer of n-tetradecane and water layer

were separated by centrifugation at 3500 rpm for 20 min at 4oC. Un-inoculated medium

served as controls and were treated in the same manner. Analytical methods

Cells growth was measured turbidimetrically at 660 nm. The cell concentration was

determined from the linear relationship between the optical density at 660 nm (OD660) and

dry cells weight (drying at 105oC for 36 h). Measurements of DBT were performed using

GC with a flame ionization detector (GC-FID). The concentrations of DBT in growth culture were analyzed by GC-17A (Shimadzu, Kyoto, Japan). Samples for GC analysis were acidified to pH 2.0 with 1 M HCl and extracted from aqueous cell/DBT suspensions

by liquid–liquid extraction using ethyl acetate in a 2:1 ratio. A portion of the ethyl acetate

layer was removed and centrifuged and 1 µl of the supernatant was injected into a gas chromatograph. The gas chromatograph was equipped with a fused silica capillary column, CBPI-m25-025 (25 m 0.22 mm id, df ¼ 0.25 l), packed with silicone OV-1, SE-30 (Shimadzu, Tokyo, Japan). The flow rate of helium carrier was 1 ml/min. The column temperature was programmed from 140 to 250ºC at 8ºC/min. The injector and detector temperatures were maintained at 280 and 310ºC, respectively.

RESULTS AND DISCUSSIONS

Temperature-dependent desulfurization of DBT by growing cells of KWN5

The temperature is a major environmental factor that affecting physiological activity of most prokaryotes. At optimum temperature, microbes perform biological activities at the maximum rate such as growth and metabolism. The effects of temperature on DBT degradation by growing cells of KWN5 were examined 96 hours cultivation under different temperatures. As shown in Fig. 1, KWN5 grew significantly in the MSSF medium containing 200 ppm DBT in tetradecane as the sole source of sulfur. Moreover, growing cells of KWN5 exhibited high desulfurizing ability toward 200 ppm DBT in TD over a wide temperature range from 27 to 47°C, and this was most efficient from 32 to 37°C. From the results, it was clearly shown that microbial growth of KWN5 strain at 37°C resulted the highest growth and desulfurizng activity. In that condition showed that the sulfur content in model oil decreased from 200 to 55.74 ppm DBT (72,13% degradation) over 4 days incubation. However, the activity suddenly decreased at 42°C. In contrast, no reduction of sulfur was detected for the un-inoculated samples after treatment under the

same conditions. Kirimura et al., (2001) also reported that B. subtilis WU-S2B also

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FIG. 1. Effects of temperature on DBT desulfurization by growing cells of KWN5 strain. KWN5 was cultivated in MSSF medium with 200 ppm DBT as sole source of

sulfur at various temperatures for 96 hours. Symbols: ◆, growth (OD660), and ▲,

DBT degradation.

Effect of various initial pHs on the growth and desulfurization activity

The effect of initial pH towards growth and desulfurization activity of KWN5 was demonstrated in Figur 2. Growth of KWN5 was studied over a wide range of pH, ranging from 6.0 until 8.0, and the maximal growth and desulfurization activity were obtained at

pH 7.0. The growth rate (OD660) and desulfurizing activity of KWN5 strain in pH 7.0

medium were 1.2 and 75.21%, respectively. The activity of KWN5 sharply decreased was observed when the bacteria were grown in the medium with initial pH at lower and higher then pH 7. However, growth of bacteria was not significantly affected by pH.

The result was almost same with other desulfurizing bacteria such as S. subarctica T7b

(Gunam et al. 2006), Gunam et al. 2011. Gunam et al. (2006) reported that S. subarctica

T7b had optimal growth and desulfurization activities when the value of pH was 7. When the pH changes from 6.5 to 7.5, the degradation rate of DBt by KWN5 strain was kept at about 72-75%. Whereas the degradation ability of the suspended cells was only 30-34%. Meanwhile, the suspended cells lost more than 40% activity when the pH was lower than 5.5.

FIG. 2. Effects of initial pH on DBT degradation by growing cells of KWN5 strain. KWN5 was cultivated in MSSF medium with 200 ppm DBT as sole source of

sulfur at various pH for 96 hours. Symbols: ◆, growth (OD660), and ▲, DBT

degradation.

CONCLUSIONS

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Pseudomonas sp. Strain KWN5 was great potential in degrading aromatic sulfur compound contained in petroleum, it is necessary to conduct further research especially to choose an effective method in its application in industry.

REFERENCES

Furuya T, Ishii Y, Ken-ichi Noda, Kino, K and Kirimura K. 2003. Thermophilic

biodesulfurization of hydrodesulfurized light gas oils by Mycobacterium phlei WU-F1,

FEMS Microbiology Letters 221:137-142.

Guerinik K2 and Al-Mutawah Q. 2003. Isolation and characterization of oil-desulfurizing

bacteria. World Journal of Microbiology and Biotechnology 19, 941–945.

Gunam IBW, Yaku Y, Hirano M, Yamamura K, Tomita F, Sone T and Asano K. 2006. Biodesulfurization of alkylated forms of dibenzothiophene and benzothiophene by

Sphingomonas subarctica T7b. Journal of Bioscience and Bioengineering 101, 322-327.

Gunam IBW, Duniaji AS, dan Triani IGAL. 2009. Biodesulfurisasi minyak bumi dengan menggunakan bakteri pendegradasi sulfur dengan teknik sel terimobilisasi. Laporan Penelitian Hibah Bersaing Tahap II. Universitas Udayana.

Gunam IBW, Duniaji AS, and Triani IGAL, and Sitepu A. 2011. Biodeslfurization of

dibenzothiophene by growing and immobilized cells of KWN5 strain. 3rd International

Conference on “Maintaining World Prosperity Through Bioscience, Biotechnology and Revegetation ”, Depasar, Bali, Indonesia, 21-22 September 2011.

Jasrizal DC. 2009. Deskripsi Dokumen: Biodesulfurisasi Minyak bumi Sebagai Upaya

Pengurangan Pencemaran Lingkungan. Tesis S2. http://www.digilib.

ui.ac.id//opac/themes/libri2/detail.jsp?id=92772&lokasi=lokal. Diakses Tanggal 28 Februari 2010.

Kirimura K, Furuya T, Nishii Y, Ishii Y, Kino K, and Usami S. 2001. Biodesulfurization of dibenzothiophene and its derivates through the selective cleavage of carbon-sulfur

bonds by a moderately thermophilic bacterium Bacillus subtilis WU-S2B. J. Biosci.

Bioeng. 91: 262-266.

Laras BK. 2006. Pencemaran Oleh Hujan Asam Dalam Konteks Kebijakan Global. http://www.rudyct.com/PPS702-ipb/12167/bambang_kl.pdf. Diakses tanggal 30 Juni 2010.

Schiller JE, and Mathiason DR. 1997. Separation method for coal-derived solids and heavy

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Gambar

FIG. 2. Effects of initial pH on DBT degradation by growing cells of KWN5 strain.   KWN5 was cultivated in MSSF medium with 200 ppm DBT as sole source of sulfur at various pH for 96 hours

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