TY - JOUR AU - Liu, H Z AB - Abstract The immobilization of Pseudomonas delafieldii R-8 in calcium alginate beads has been studied in order to improve biodesulfurization activity in oil/water (O/W) biphasic systems. A gas jet extrusion technique was performed to produce immobilized beads. The specific desulfurization rate of 1.5 mm diameter beads was 1.4-fold higher than that of 4.0 mm. Some nonionic surfactants can significantly increase the activity of immobilized cells. The desulfurization rate with the addition of 0.5% Span 80 increased 1.8-fold compared with that of the untreated beads. The rate of biodesulfurization was markedly enhanced by decreasing the size of alginate beads and adding the surfactant Span 80, most likely resulting from the increasing mass transfer of substrate to gel matrix. Introduction With stricter environment regulations and steady increases in the average sulfur content of petroleum, refiners are facing major challenges to developing new design approaches to ultra-low sulfur diesel fuels [24]. Presently, biodesulfurization (BDS) has attracted intensive interest due to its benefits of cost-effective, mild reaction conditions, and low impact on the environment [5, 8, 11, 19]. Dibenzothiophene (DBT) is usually considered as the model compound for biodesulfurization research. There are numerous reports on the treatment of diesel oils or model oil mixtures by using suspensions of growing or resting cells [3, 15, 18, 20, 27]. Nevertheless, the treatment of oils using free cells has some limitations such as high cost of the biocatalyst and low volumetric ratio between the organic phase and the aqueous one. Also, separation of product oil from oil–water-biocatalyst emulsion is very troublesome [4, 14]. From the point of industrial application of BDS, cell immobilization was considered to be one of the most promising approaches [22]. So far, very few published papers are available on BDS by immobilized cells [2, 7, 9]. Calcium alginate is currently one of the most widely used entrapment carriers for immobilization of enzymes and whole cells for its advantages of biocompatibility, cheapness and simplicity [10, 16]. However, the entrapment technique often leads to a decrease of biocatalytic activity, mostly caused by diffusional limitations and steric hindrance [6, 7, 13]. The existence of diffusional limitations reduces the catalytic efficiency of immobilized biocatalysts and therefore should be minimized. Herein, immobilization of resting cells of Pseudomonas delafieldii R-8 was conducted by entrapment in calcium alginate. The kinetics of biodesulfurization by the alginate immobilized cells was analyzed. In the present study, a simple cell-immobilization technology was developed, aiming to increase the biodesulfurization rate of immobilized biocatalysts in oil/water biphasic systems. It was achieved by decreasing the size of alginate beads and adding Span 80 in the bead-forming process. Improvements in the rate of biodesulfurization were possibly due to the improvement of mass transfer rate of substrate and reduced product inhibition. Materials and methods Chemicals Dibenzothiophene (DBT) and Span 80 (Sorbitan monooleate) were purchased from Acros Organics (US). 2-Hydroxybiphenyl (2-HBP) and n-dodecane were purchased from Tokyo Kasei Kogyo Co., Ltd. (TCI; Japan). Tween 20 (Polyoxyethylene sorbitan monolaurate) was purchased from Fluka Chemika (Switzerland). Sodium alginate, Span 20 (Sorbitan monolaurate), Tween 80 (Polyoxyethylene sorbitan monostearate) were purchased from Beijing Chemical Reagents Company (China). Methanol was liquid chromatography grade. Sodium dodecyl sulfate (SDS), Cetyl trimethyl ammonium bromide (CTAB), Triton X-100 (polyethylene glycol p-tert-octylphenyl ether) and other materials were analytical grade and were available commercially. Bacterial strain and cultivation Pseudomonas delafieldii R-8 (CGMCC No. 0570) was isolated from the sewage pool of Shengli oil field of China, and was capable of desulfurizing DBT to 2-HBP [7, 23]. The cells were incubated in 500 mL flasks containing 120 mL basal salt medium (BSM) supplemented with 0.2 mmol/L DBT as the source of sulfur. Cell cultivation was carried out at 30 °C on a rotary shaker operated at 180 rpm (THZ-C rotary shaker, Taicang city, Jiangsu province, China). The inoculum size was 2% (v/v). The BSM was composed of KH2PO4 2.44 g, Na2HPO4·12H2O 12.03 g, NH4Cl 2.0 g, MgCl2·6H2O 0.4 g, CaCl2 0.75 mg, FeCl3·6H2O 1 mg, MnCl2·4H2O 4 mg and glycerol 10 g in one liter of deionized water. Cell immobilization in calcium alginate beads Cells were harvested in the late exponential phase by centrifugation at 5,000 × g for 5 min. The harvested cell pellets were washed twice with deionized water and suspended in it. Sodium alginate was dissolved in deionized water (4%, w/v) and mixed well with equal volume of cell suspension. Certain amounts of surfactant such as Tween 20, Tween 80, Span 80, etc. were added respectively into the mixture. The target concentration of these surfactants was set at 0.5% (w/v). We used conventional methods to yield 2–5 mm beads by extruding the alginate as drops into a calcium salt solution for gelation. The gas jet extrusion technique, which was modified from Seifert and Phillips [21], was employed to produce smaller alginate beads. The bead fabrication procedure with a novel instrument is illustrated in Fig. 1. The resultant slurry was extruded through a cone-shaped needle into a stirred 0.1 M CaCl2 gelling solution. The slurry is intruded as discrete droplets so as to form calcium-alginate beads with normal size (2.5 and 4 mm in diameter). To prepare smaller beads than 2 mm diameter, nitrogen gas was introduced around the tip of the needle to blow off the droplets. By adjusting the gas flow rate to 0.5 L/min, the size of the beads can be controlled at 1.5 mm in diameter. Fig. 1 Open in new tabDownload slide Procedure for preparation of calcium-alginate beads The beads were left in calcium chloride solution about 2 h for stabilization. Then, the beads were washed with deionized water to remove the residual calcium ions and then kept in saline at about 4 °C. Before being used, immobilized cells were activated for 1 day in modified BSM (MBSM) supplemented with 0.1 mmol/L DBT. Activation was carried out at 30 °C on a 180 rpm rotary shaker (THZ-C rotary shaker, Taicang city, Jiangsu province, China). To avoid the dissolution of alginate-immobilized cells in the BSM, MBSM was used as the aqueous phase for the activation of the immobilized cells. The phosphate components of MBSM were changed to KH2PO4 0.24 g and Na2HPO4·12H2O 1.20 g. Other components were the same as those in BSM. Biodesulfurization in model oil We prepared model oil consisting of 1 mmol/L DBT in n-dodecane. The reaction solution contained alginate-immobilized cells (6 g beads, containing 0.15 g of dry cells), 5 mL of model oil and 10 mL of MBSM medium. Unless otherwise stated, the size of beads used in experiments was 2.5 mm. Biodesulfurization was carried out in 100 mL flasks at 30 °C on a rotary shaker at 180 rpm (THZ-C rotary shaker, Taicang city, Jiangsu province, China). The time course of DBT utilization and 2-HBP productions were obtained by sampling at defined time intervals for analyzing with HPLC. After reaction, the beads were separated from the model oil by a stainless steel sieve and regenerated in MBSM medium for recycle desulfurization. The regeneration procedures were the same as the activation described before. All experiments were conducted in triplicate. Analytical methods Cell density was calculated from the absorbance at 600 nm, with reference to a calibration curve constructed with scalar dilutions of a cell suspension of known density. One optical unit for the R-8 cells was equivalent to 0.395 g dry weight/L. The cell density within Ca-alginate beads was determined after dissolving the beads in a 0.5 mmol/L EDTA solution with continuous stirring. To determine the average size of the alginate beads, ten individual beads were measured with vernier calipers. High-performance liquid chromatography (HPLC) was used for the quantitative assay of DBT (retention time = 5.94 min) and 2-HBP (retention time = 3.45 min) in the dodecane phase. HPLC was performed on a Hewlett Packard 1100 (HP1100, Agilent, USA) liquid chromatography equipped with an autosampler, a reversed-phase Kromasil-C18 column (250 × 4.6 mm; 5 μm) and a diode array detector (set at 254 nm). The mobile phase was composed of methanol–water (90:10, v/v) with flow rate of 1 mL min−1. The specific desulfurization activity was expressed as the production rate of 2-HBP, which is the end product of the DBT degradation pathway. The morphology of alginate-immobilized cells was determined using a scanning electron microscope (SEM) (JSM-6700F, JEOL, Japan). Results Effect of the size of immobilized beads on BDS Desulfurization of DBT was carried out with different sizes of alginate-immobilized beads in the presence of n-dodecane. Table 1 shows the results of DBT remaining and 2-HBP produced in 24 h of reaction. The mean diameters of the immobilized beads were 1.5, 2.5 and 4.0 mm. The results demonstrated that the desulfurization of DBT by alginate-immobilized cells was affected by the size of the immobilized beads. The specific desulfurization rate of 1.5 mm diameter beads was 1.4-fold higher than that of 4.0 mm. Klein et al. [12] reported that a small microbead size is important for minimizing the mass-transfer resistance problem normally associated with immobilized cell culture. The desulfurization rate was improved with decreasing bead size, most probably due to the minimizing of the mass transfe barrier r. Effect of bead size (diameter) on biodesulfurization rate by alginate-immobilized cells of P. delafieldi i R-8 Bead size (mm) . 2-HBP production (mmol/L) . DBT residue (mmol/L) . Specific desulfurization rate (mmol L−1 h−1) . 1.5 0.327 0.409 1.36 × 10−2 2.5 0.286 0.445 1.19 × 10−2 4.0 0.237 0.510 0.99 × 10−2 Bead size (mm) . 2-HBP production (mmol/L) . DBT residue (mmol/L) . Specific desulfurization rate (mmol L−1 h−1) . 1.5 0.327 0.409 1.36 × 10−2 2.5 0.286 0.445 1.19 × 10−2 4.0 0.237 0.510 0.99 × 10−2 * Reaction conditions: 6 g beads. Volume ratio of oil-to-water was 0.5, 24 h of reaction Open in new tab Effect of bead size (diameter) on biodesulfurization rate by alginate-immobilized cells of P. delafieldi i R-8 Bead size (mm) . 2-HBP production (mmol/L) . DBT residue (mmol/L) . Specific desulfurization rate (mmol L−1 h−1) . 1.5 0.327 0.409 1.36 × 10−2 2.5 0.286 0.445 1.19 × 10−2 4.0 0.237 0.510 0.99 × 10−2 Bead size (mm) . 2-HBP production (mmol/L) . DBT residue (mmol/L) . Specific desulfurization rate (mmol L−1 h−1) . 1.5 0.327 0.409 1.36 × 10−2 2.5 0.286 0.445 1.19 × 10−2 4.0 0.237 0.510 0.99 × 10−2 * Reaction conditions: 6 g beads. Volume ratio of oil-to-water was 0.5, 24 h of reaction Open in new tab Influence of the addition of surfactants on desulfurization rate The influence of surfactants on the immobilized cells was evaluated by comparing the conversion of DBT into 2-HBP in model oil systems. Figure 2 compares 2-HBP production by immobilized cells treated with seven different kinds of surfactants, while an immobilization procedure with no surfactant served as the control. The production of 2-HBP mostly occurred in the first day. The addition of non-toxic and non-ionic surfactants including Span 20, Span 80, Tween 20 and Tween 80 greatly enhanced the desulfurization rate compared to the control. However, the addition of CTAB and SDS decreased the production of 2-HBP. As shown in Fig. 2, Span 80 showed the highest effect on desulfurization activity. Fig. 2 Open in new tabDownload slide Effect of different surfactants on the desulfurization activity of immobilized beads. Reaction conditions: 2.5 mm bead diameter, model oil (1 mmol/L DBT in n-dodecane), O/W (v/v) = 1/2, 2 days of reaction Selection of optimal concentration of Span 80 In order to select the optimal concentration of Span 80 with respect to the desulfurization rate, further experiments were carried out. Calcium-alginate beads prepared with different Span 80 concentrations were used for biodesulfurization in oil-water systems. Figure 3 shows the influence of Span 80 on 2-HBP production. It can be observed that the 2-HBP production increased with Span 80 concentration. Optimal desulfurizing capability was obtained when the Span 80 concentration was controlled between 0.4 and 0.7%. In 24 h, the desulfurization rate with the addition of 0.5% Span 80 was 1.8-fold higher than that of without Span 80. Fig. 3 Open in new tabDownload slide Desulfurization activity of alginate beads treated with different concentrations of Span 80 Scanning morphology of calcium-alginate beads In order to understand cells distribution in calcium-alginate beads with Span 80, the sections of the beads after being repeatedly used for three times were observed by SEM. The results are shown in Fig. 4. A few P. delafieldii R-8 cells were observed on the surface of gel beads (Fig. 4a) and a highly macroporous structure was found in the beads which may favor of diffusion of substrates and dissolved gas. Large numbers of cells were evident within the Internet structures of the beads (Fig. 4b). Pseudomonas delafieldii R-8 cells appeared to be entrapped and maintained their structural integrity within the gel matrix. Fig. 4 Open in new tabDownload slide SEM of alginate-immobilized cells of R-8 after 150 h of desulfurization of model oil a Surface of alginate-immobilized cells; b Cross section of alginate-immobilized cells Kinetics of biodesulfurization by alginate immobilized cells Many kinetic analyses of biodesulfurization have been performed using free cells [26]. However, there are few reports on the kinetics of biodesulfurization by immobilized cells, especially, alginate-immobilized cells. In this work, we compared the kinetic parameters of desulfurization using alginate immobilized R-8 cells with or without addition of Span 80. The reaction systems were consisted of 6 g new activated immobilized beads (or 0.15 g dry cells), 20 mL MBSM medium and 10 mL model oil. The initial desulfurization rate was studied with various DBT concentrations in model oil (Fig. 5). The results could be represented by the Michaelis–Menten equation, as follows: $$ \upsilon = - \frac{{{\text{d}}S}} {{{\text{d}}t}} = \frac{{V_{{\max }} S}} {{K_{m} + S}} $$ where S, concentration of DBT (mmol L−1); V max, the limiting maximal velocity (mmol L−1 h−1, or μmol/g DCW/h); K m, Michaelis constant (mmol L−1). Fig. 5 Open in new tabDownload slide Kinetics of desulfurization of DBT by the free and immobilized R-8 cells. The reaction was performed in O/W biphasic systems As shown in Fig. 5, both the K m values of the free and immobilized cells were equivalent and were found to be 1.65 mmol L−1. The V max value of immobilized cells was less than the value of free cells. The V max value of the immobilized cells with Span 80 was 0.34 mmol L−1 h−1, and that of the control was 0.22 mmol L−1 h−1. The V max value of the free cells was 0.42 mmol L−1 h−1. The Michaelis constants, an intrinsic parameter of cells, are not affected by the immobilization process, while the maximal desulfurization rates are affected. Discussion Immobilized enzymes and whole cells as biocatalysts provide advantages such as enhanced stability, repeated or continuous use, easy separation from the reaction mixture and possible modulation of catalytic properties. Immobilization has become an indispensable part of industrial biotransformations [17]. The study of immobilized whole cells would give a solution to the problem in petroleum biodesulfurization, such as the troublesome process of recovering desulfurized oil and the short life of biocatalyst. Hou et al. [9] reported that the maximal desulfurization rate of immobilized cells was lower than that of non-immobilized cells. The main advantages of immobilized cells could be repeated and convenient operations. As with most immobilization systems, the diffusional rate of substrates and products within the bead often limits productivity. Mass transfer involved in diffusion of a substrate to a reaction site and in removal of inhibitory or toxic products from the environment may be impeded. With the gas jet extrusion technique, we successfully prepared alginate-immobilized beads for biodesulfurization. This method was rapid and simple. As we have proved, the obvious approach to minimize these effects is to minimize the diffusional distance through a reduction in bead size [1]. Song et al [25] have employed Tween 20 to improve the permeability of the entrapment–encapsulation hybrid membrane. According to Ref. [25], the immobilized beads without Tween 20 would rupture because of the formation of CO2 and N2 as result of respiration and denitrification. In our study, we found that Span 80 and Tween 20 can significantly increase the desulfurization activity of immobilized cells. The specific desulfurization activity of various cultures was described in the literature [11]. But there is no report on the activity of immobilized cells. In the Michaelis–Menten equation, the change of V max may result from the differences of nutriments, substrates and metabolites diffusion between the immobilized beads with or without addition of Span 80. Therefore, the V max value of control (15 μmol/g DCW/h) was less than the V max value of Span 80 (23 μmol/g DCW/h). Thus, the use of Span 80 in cell immobilization is beneficial, increasing permeability and mass transfer and resulting in a higher biocatalytic activity. To improve biodesulfurization rate of immobilized cells is a key to industrialize biodesulfurization technology. We employed a simple way by decreasing the beads size and adding Span 80 to achieve the purpose. The encouraging results of this work may be generally applicable to other area of biocatalytic and biotransformation processes. Acknowledgments This work was financially supported by the National High Technology Research and Development Program of China (No. 20060102Z2042), and the State Major Basic Research Development Program of China (No. 2006CB202507). References 1. Cassidy MB , Lee H, Trevors JT Environmental applications of immobilized microbial cells: a review J Ind Microbiol Biotechnol 1996 16 79 101 Google Scholar OpenURL Placeholder Text WorldCat 2. Chang JH , Chang YK, Ryu HW, Chang HN Desulfurization of light gas oil in immobilized-cell systems of Gordona sp. CYKS1 and Nocardia sp. CYKS2 FEMS Microbiol Lett 2000 182 309 312 10.1111/j.1574-6968.2000.tb08913.x Google Scholar Crossref Search ADS PubMed WorldCat 3. Chang JH , Kim YJ, Lee BH, Cho KS, Ryu HW, Chang YK, Chang HN Production of a desulfurization biocatalyst by two-stage fermentation and its application for the treatment of model and diesel oils Biotechnol Prog 2001 17 876 880 10.1021/bp0100676 Google Scholar Crossref Search ADS PubMed WorldCat 4. Choi OK , Cho KS, Ryu HW, Chang YK Enhancement of phase separation by the addition of de-emulsifiers to three-phase (diesel oil/biocatalyst/aqueous phase) emulsion in diesel biodesulfurization Biotechnol Lett 2003 25 73 77 10.1023/A:1021750719337 Google Scholar Crossref Search ADS PubMed WorldCat 5. Gray KA , Pogrebinsky OS, Mrachko GT, Xi L, Monticello DJ, Squires CH Molecular mechanisms of biocatalytic desulfurization of fossil fuels Nat Biotechnol 1996 14 1705 1709 10.1038/nbt1296-1705 Google Scholar Crossref Search ADS PubMed WorldCat 6. Gunther K , Helmut S Immobilization of Proteus vulgaris for the reduction of 2-oxo acids with hydrogen gas or formate to d-2-hydroxy acids Appl Microbiol Biotechnol 1993 38 441 446 Google Scholar OpenURL Placeholder Text WorldCat 7. Guobin S , Jianmin X, Chen G, Huizhou L, Jiayong C Biodesulfurization using Pseudomonas delafieldii in magnetic polyvinyl alcohol beads Lett Appl Microbiol 2005 40 30 36 10.1111/j.1472-765X.2004.01617.x Google Scholar Crossref Search ADS PubMed WorldCat 8. Gupta N , Roychoudhury PK, Deb JK Biotechnology of desulfurization of diesel: prospects and challenges Appl Microbiol Biotechnol 2005 66 356 366 10.1007/s00253-004-1755-7 Google Scholar Crossref Search ADS PubMed WorldCat 9. Hou YF , Kong Y, Yang JR, Zhang JH, Shi DQ, Xin W Biodesulfurization of dibenzothiophene by immobilized cells of Pseudomonas stutzeri UP-1 Fuel 2005 84 1975 1979 10.1016/j.fuel.2005.04.004 Google Scholar Crossref Search ADS WorldCat 10. Houng JY , Chiang WP, Chen KC, Tiu C 11 α-Hydroxylation of progesterone in biphasic media using alginate-entrapped Aspergillus ochraceus gel beads coated with polyurea Enzyme Microb Technol 1994 16 485 491 10.1016/0141-0229(94)90018-3 Google Scholar Crossref Search ADS PubMed WorldCat 11. Kilbane JJ II Microbial biocatalyst developments to upgrade fossil fuels Curr Opin Biotechnol 2006 17 305 314 10.1016/j.copbio.2006.04.005 Google Scholar Crossref Search ADS PubMed WorldCat 12. Klein J , Stock J, Vorlop KD Pore size and properties of spherical Ca-alginate biocatalysts Eur J Appl Microbiol Biotechnol 1983 18 86 91 10.1007/BF00500829 Google Scholar Crossref Search ADS WorldCat 13. Klibanov AM Immobilized enzymes and cells as practical catalysts Science 1983 219 722 727 10.1126/science.219.4585.722 Google Scholar Crossref Search ADS PubMed WorldCat 14. Konishi M , Kishimoto M, Tamesui N, Omasa I, Shioya S, Ohtake H The separation of oil from an oil–water–bacteria mixture using a hydrophobic tubular membrane Biochem Eng J 2005 24 49 54 10.1016/j.bej.2004.11.012 Google Scholar Crossref Search ADS WorldCat 15. Labana S , Pandey G, Jain RK Desulphurization of dibenzothiophene and diesel oils by bacteria Lett Appl Microbiol 2005 40 159 163 10.1111/j.1472-765X.2004.01648.x Google Scholar Crossref Search ADS PubMed WorldCat 16. Leon R , Fernandes P, Pinheiro HM, Cabral JMS Whole-cell biocatalysis in organic media Enzyme Microb Technol 1998 23 483 500 10.1016/S0141-0229(98)00078-7 Google Scholar Crossref Search ADS WorldCat 17. Liese A , Seelbach K, Wandrey C Industrial biotransformations 2006 2nd Completely Revised and Enlarged Edition Hoboken Wiley-VCH Google Scholar Crossref Search ADS Google Preview WorldCat COPAC 18. Maghsoudi S , Vossoughi M, Kheirolomoom A, Tanaka E, Katoh S Biodesulfurization of hydrocarbons and diesel fuels by Rhodococcus sp strain P32C1 Biochem Eng J 2001 8 151 156 10.1016/S1369-703X(01)00097-3 Google Scholar Crossref Search ADS WorldCat 19. McFarland BL , Boron DJ, Deever W, Meyer JA, Johnson AR, Atlas RM Biocatalytic sulfur removal from fuels: applicability for producing low sulfur gasoline Crit Rev Microbiol 1998 24 99 147 10.1080/10408419891294208 Google Scholar Crossref Search ADS PubMed WorldCat 20. Noda KI , Watanabe K, Maruhashi K Isolation of a recombinant desulfurizing 4,6-dipropyl dibenzothiophene in n-tetradecane J Biosci Bioeng 2003 95 354 360 Google Scholar Crossref Search ADS PubMed WorldCat 21. Seifert DB , Phillips JA Production of small, monodispersed alginate beads for cell immobilization Biotechnol Prog 1997 13 562 568 10.1021/bp9700723 Google Scholar Crossref Search ADS WorldCat 22. Setti L , Lanzarini G, Pifferi PG Whole cell biocatalysis for an oil desulfurization process Fuel Process Technol 1997 52 145 153 10.1016/S0378-3820(97)00023-4 Google Scholar Crossref Search ADS WorldCat 23. Shan GB , Xing JM, Zhang HY, Liu HZ Biodesulfurization of dibenzothiophene by microbial cells coated with magnetite nanoparticles Appl Environ Microbiol 2005 71 4497 4502 10.1128/AEM.71.8.4497-4502.2005 Google Scholar Crossref Search ADS PubMed WorldCat 24. Song C , Ma XL New design approaches to ultra-clean diesel fuels by deep desulfurization and deep dearomatization Appl Catal B-Environ 2003 41 207 238 10.1016/S0926-3373(02)00212-6 Google Scholar Crossref Search ADS WorldCat 25. Song SH , Choi SS, Park K, Yoo YJ Novel hybrid immobilization of microorganisms and its applications to biological denitrification Enzyme Microb Technol 2005 37 567 573 10.1016/j.enzmictec.2005.07.012 Google Scholar Crossref Search ADS WorldCat 26. Wang P , Humphrey AE, Krawiec S Kinetic analyses of desulfurization of dibenzothiophene by Rhodococcus erythropolis in continuous cultures Appl Environ Microbiol 1996 62 3066 3068 Google Scholar Crossref Search ADS PubMed WorldCat 27. Yu B , Xu P, Shi Q, Ma CQ Deep desulfurization of diesel oil and crude oils by a newly isolated Rhodococcus erythropolis strain Appl Environ Microbiol 2006 72 54 58 10.1128/AEM.72.1.54-58.2006 Google Scholar Crossref Search ADS PubMed WorldCat © Society for Industrial Microbiology 2008 This article is published and distributed under the terms of the Oxford University Press, Standard Journals Publication Model (https://academic.oup.com/journals/pages/open_access/funder_policies/chorus/standard_publication_model) © Society for Industrial Microbiology 2008 TI - Improvement of biodesulfurization activity of alginate immobilized cells in biphasic systems JF - Journal of Industrial Microbiology and Biotechnology DO - 10.1007/s10295-007-0268-7 DA - 2008-03-01 UR - https://www.deepdyve.com/lp/oxford-university-press/improvement-of-biodesulfurization-activity-of-alginate-immobilized-dF9YVYB0mi SP - 145 EP - 150 VL - 35 IS - 3 DP - DeepDyve ER -