Research Article | Open Access
Abrar Ahmad1 , Othman A. Baothman1, Muhammad Shahid Nadeem1and Varish Ahmad2
1Department of Biochemistry, Faculty of Sciences, King Abdulaziz University, Jeddah, Kingdom of Saudi Arabia.
2Department of Health Information Technology, Faculty of Applied Sciences, King Abdulaziz University, Jeddah, Kingdom of Saudi Arabia.
Article Number: 8704 | © The Author(s). 2023
J Pure Appl Microbiol. 2023;17(3):1737-1747. https://doi.org/10.22207/JPAM.17.3.39
Received: 16 May 2023 | Accepted: 28 July 2023 | Published online: 02 September 2023
Issue online: September 2023
Abstract

Gordonia sp., Rhodococcus, Paenibaccilus, Mycobacterium and many other desulfurizing strains have shown good potential for dibenzothiophene (DBT), 4, 6-Dimethyldibenzothiophene (4-6-Dimethyl dibenzothiophene) and other organosulfur biodesulfurization. These are microbes which have 4S pathway to remove S from remaining calcitarant organosulfur compounds even after deep desulfurization. Sulfur compounds present in crude oils, diesel and petrol when combust in engines they emerge out in the form of elemental Sulfur, which causes environmental and health problems. Therefore, efforts are going to remove this Sulfur compounds by Hydrodesulfurization (HDS) treatment. Some organosulfur compounds remain there even after HDS, which can only remove by highly evolved microbes residing nearby petroleum-contaminated areas in refineries zone. Nature has such adopted and evolved microbes for the bioremediation of such toxic substances. Here we have isolated and characterized highly evolved and adopted Biodesulfurizing microbes present around oil refineries in Kingdom of Saudi Arabia and prepare the culture collection of such highly evolved and adopted biodesulfurization microorganisms for future application of applied Industrial petroleum refineries, which can reduce the Sulfur load in the petroleum products. The several (10 different types) microbes have been reported in these soils to grow in sulfur compounds. Out of these microbes one microbe desulfurizes by 4S pathway. It was identified to be Rhodococcus erythropolis type named as Rhodococcus erythroplis KAU10. They show good potential for various organosulfur compounds (DBT, 2,4,6-Trimethyl Benzothiophene, Benzothiophene, Dibenzyl sulfide, Benzonaphthothiophene, Dibenzothiophene sulfone, along with crude oil and Petrol and Diesel. Isolated strain Rhodococcus erythroplis KAU10 have good potential for Biodesulfurization.

Keywords

Biodesulfurization, Isolation, Characterization, Rhodococcus erythroplis KAU10, 4S Pathway

Introduction

Since GCC countries are Oil/Fossil, fuel-based countries. The major economy of these countries is based on oil production, refining, and its export to other countries. Nearly 70% of the all-energy oil reserves are from Gulf region. At this time, the confirmed petroleum reserves in the GCC countries account for 30% of the total. At 15.7%, Saudi Arabia is in the lead, accompanied by Kuwait at 6%, the UAE at 5.7%, Qatar at 1.5%, Bahrain at 0.4%, and Oman at 0.3%. In 2022, the GCC nations collectively produced 28.6 million barrels per day, or 32.3% of total global output. Although all GCC nations are impacted by decreasing oil prices, not all are impacted equally. Oman and Bahrain are most impacted by the reduction in oil costs, while Qatar, the United Arab Emirates (UAE), Kuwait and Saudi Arabia (KSA) are not as impacted.1 As the demand for oil utilization is increasing, the conventional oil well’s supplies are decreasing and expected to be exhausted by the end of 2070, so we have to rely on non-convention oil which have more sulfur percentage (Sour crude oil), so it is important to remove sulfur from these oils because they are harmful to the human health, atmosphere, and refinery machines (catalyst used in refining). For sulfur removal, the very old and tradition method is the chemical method where all most all sulfur compounds are removed, but recalcitrant organosulfur compounds remain there even after HDS which after combustion in engines creates environmental problems to human being directly or indirectly. Interesting thing is there that microbes can remove these recalcitrant organosulfur compounds by either reduction method (Kodama pathway) or oxidation method 4S-pathway.2-6 In Kodama, pathway fuel value is not conserved, while in 4S pathway fuel value of carbon is conserved. 4S pathway is the preferred way of desulfurization because of saving calorific value of organosulfur compounds in industrial perspective. Thermophilic bacteria have also been reported showing the 4S pathways.7-9 In 4S pathway, phenolic products are formed as the product10-17 as shown in Scheme 1. As the accumulation of product increases, the activities of this pathway enzyme get decreased/ceased. That is why industrial application of this pathway could not be possible. If we could remove this inhibition by Biotechnological or by Molecular approach, thinks would be easier to apply at industrial scale.18,19 Here we isolated and characterized Biodesulfurizing microbes from the various oil refineries areas in Saudi Kingdom. Here the measure work was emphasized on potential microbes to be isolated which could fulfil the demand of biodesulfurization of various organosulfur compounds, which remains even after HDS. If the diversity of the microbes is studied and fully characterised, the best quality microbes in terms of biodesulfurization properties, can be made even better by metabolic engineering to remove inhibition by this phenolic product in Saudi Arabia.20-22 Its industrial scale application can be possible for desulfurization. Crude oil, diesel and petrol may be more precious and valuable for GCC countries, once all the recalcitrant organosulfur compounds are removed or desulfurized23 by highly evolved microbes from Saudi region. It can boost and enhance the economy of GCC countries by providing sulfur free petroleum products to the Global market. The isolated microorganism identified to be Rhodococcus erythropolis KAU10 by morphological, Biochemical, Analytical methods and 16S rRNA gene-based sequencing methods. This strain can grow on various organosulfur compounds and have 4S pathway for biodesulfurization. This strain has potential to be used in Industrial level Biodesulfurization.

Scheme 1. 4S pathway for DBT desulfurization using DszA, DszB, DszC and DszD enzymes

Materials and Methods

Chemicals and materials
All the analytical grade chemicals (DBT, 2-HBP, BT, DBT-sulfone, Gibb’s reagents) were obtained from Sigma-Aldrich company. All the chemicals were highly pure (99%) and analytical grade. Media like Luria broth, Agar Powder, Agarose Powder, Gram-staining and bacterial identification kits were purchased from High-Media company. Molecular based chemicals and reagents were purchased from Sigma company. Acetone, Methanol, Ethenol, Ethyl acetate and n-hexane extra pure (99%) were purchased from Merck company.

Overview of Methodologies used
Soils from two different locations were taken for isolation for desulfurzing microbes via 4S pathway. Soil samples were incubated with media containing DBT and incubated for 5 days of each cycles. After 5 weeks of such cycles, bacteria cultures were taken for Gibb’s assay by spectrophotometrically. Consequently culture were spread on BSM-Agar media to get the pure colony of doing desulfurization via 4S pathway. Subsequently pure colony were identified by morphologically, biochemically and molecular biologically. Metabolites were identified by GC-MS method and its resting cell activity were compared with Rhoococcus erythropolis IGTS culture.

Bacteria isolation from DBT-grown cultures
Different crude oil resource locations in Jeddah, Saudi Arabia, were chosen and given the designations 1 and 2 in order to isolate Dibenzothiophene desulfurizing bacteria. 1 was the Jeddah Industrial Area near the refinery at the Jeddah Islamic Sea Port. The area surrounding Jeddah Airport, which has a large oil reserve basin, is where Location 2 (Second Location) was found. Samples of the oil-contaminated soil from these sites were taken in a number of places (10 locations). Each location’s sample (50 g) was combined into a single master blend. To isolate DBT-desulfurizing bacteria, 10 mL of the suspension was mixed to 100 mL of basic salt medium (BSM) in a 250 mL flask. As a source of carbon, glucose (5 g/L) and sulfur source from DBT (5 mM/L) were added to this medium. The five-day growth period took place in a spinning shaker at 30 degrees Celsius. When the BSM agar medium had been supplied with glucose and DBT, the culture broth medium was transferred on top of the BSM agar medium after such 5 subcultures.24 Samples from Workshops were used to isolate all the representative bacterial cultures that were viable and growing primarily.

4S pathway screening by Gibb’s assay test
The existence or lack of the 4S pathway in the recovered cultures was discovered by measuring 2-HBP, the pathway’s ultimate product, using the Gibb’s test. BSM broth containing glucose and DBT was used to cultivate the recovered colonies. After cultivating the bacteria in a DBT-containing medium, the amount of 2-HBP they produced was measured. When Gibb’s reagent is combined with aromatic hydroxyl groups, like 2-hydroxy phenyl, a blue complex is generated. Each bacterial culture broth had its pH adjusted to 8.0 with 10% sodium bicarbonate or sodium carbonate, and then 100 μL of each broth was combined with Gibb’s reagent (10 mg of 2,6-dichlorquinone-4-chlorimide generated in 1 mL of ethanol) for a 30-minute incubation. The findings of the Gibb’s test are displayed through the production of a blue color complex (indicating a positive result) or a brown hue (indicating a negative result). It was expected that Gibb’s assay-positive cells would produce 2-HBP from DBT via the 4S pathway.25

Analytical analysis of DBT-based metabolites from bacterial isolates (GC-MS)
After centrifuging the culture broth, the resulting supernatant was adjusted to a pH of 2.0 using 6N hydrochloric acid as the solution. Samples were extracted using the acidified supernatant and ethyl acetate in equal volumes before being analyzed by GC-MS. The Pegasus HT TOFMS was coupled with the GC in the Agilent 7890A GC-MS system. The GC column has the following dimensions: 29.8 m x 0.2 m x 320 m. The sample temperatures ranged from 60 to 320 degrees Celsius throughout the duration of the examination. The temperature increased at a rate of 15 degrees Celsius per minute while the sample was being analyzed. Throughout the entire sample, the temperature remained stable at 280 degrees Celsius. 1μL of DBT culture broth was analyzed in which 1.2 mL/min of helium is used as the carrier gas.

Identification of the 4S pathway’s dsz operon genes
The desulfurization gene A (dszA) gene was amplified using the forward primer 5′- GCGCGGCAAGTTCGATCTGT-3′ and the reverse primer 5′- TCCCGCAGGATGTCCTTGATC-3′. In order to amplify the desulfurization gene B (dszB) gene, we used the forward primer 5′-ATCGAACTCGACGTCCTCAG-3′ and the reverse primer 5′-TCAGGACCACAGCTACAAG3′. Primers 5′- CTGTTCGGATACCACCTCAC-3′ and 5′- GTGCCTGAAGGTGTTGCA-3′ were used for amplification of the desulfurization C (dszC) gene, respectively.26,27 Primers 5′- GCGCGGCAAGTTCGATCTGT-3′ and 5′- GTGCCTGAAGGTGTTGCA-3′ were used to amplify the desulfurization (dsz) ABC operon gene.

Bacterial isolate identification
Colony features
On DBT-containing basal salt media, bacterial isolates that use the 4S route for desulfurization grew in distinctive colonies. Each colony’s layout, hue, margin, height, and size were meticulously recorded.

Combining biochemical analysis with microscopy
The DBT desulfurizing bacteria’s morphological form, gram and spore stains were performed. The biochemical tests, which were conducted in accordance with predetermined protocols, included hydrogen sulfide production, the hydrolysis of starch, methyl red, casein, sucrose, catalase, indole, oxidase, Voges-Proskauer, lipid activity, nitrate reduction, urea hydrolysis and citrate utilizationtests.28-30

16S rRNA sequencing bacterial isolates
The bacterial isolates that tested positive for DBT desulfurization underwent 16s rRNA sequencing and phylogenetic analysis at the central facilities of our university. The primers 5′-GCAATAACAGGTCTGTGATGCCC-3′ (forward) and 5′ GCATCACAGACCTGTTATTGC-3′ (reverse) were used to amplify the 16S rRNA gene.31

Chromosomal DNA isolation
Separate pure bacterial culture transfers were made in 100 mL of BSM broth mixed with carbon source of glucose and sulfur source as dibenzothiophene in 500 mL flask in capacity, where they were shaken at 30°C for 4 days at 180 rpm. The culture broths underwent a ten-minute centrifugation at 10,000 rpm following the incubation time. Then, liquid nitrogen was used to crush 0.1 grams of the mycelium from each isolate on a spotless porcelain dish. Each isolate’s crushed mycelium was then put into a tube with 500 μL of TE buffer and lysozyme enzyme, and it was cultured there for 30 minutes at 37°C. The tube was then treated for 30 minutes at 55°C with 20 μL of proteinase K and 10 μL of SDS. The mixture was chilled shortly after the incubation period, spun for five minutes at 10,000 revolutions per minute, and then processed with a phenol-chloroform (1:1) mixture. The aqueous part of the combination had been moved to a sterile tube, and 90% of an ethyl alcohol solution was employed to produce a DNA precipitate at -20°C. The pellet of DNA was subsequently retrieved after 15 minutes of centrifuging at 8,000 rpm. Final DNA pellet was mixed in Tris-EDTA buffer, 20 μL of RNase enzyme was placed in it, and mixture was incubated for a single hour at 37 degrees Celsius to produce pure DNA witch is free from RNA contamination. The genetic material DNA was precipitated once again using ethyl alcohol (90%) at -20°C. After spinning (for 10 minutes at 10,000 rpm),32 a pure DNA pellet was produced, and the DNA’s purity was assessed using a Ultra-visible (UV) spectrophotometer.

Gene/s characterization
The Polymerase chain reaction (PCR) was done using 50 ul of buffer, 10% dimethyl sulfoxide, 6 mM magnesium chloride, 2.5 units of Taq Pol, and 30 pmol of each primer. The DNA input taken was 100 ng. Initial temperature was set at 94°C for 1 minute to denature the mixture, then it was lowered to 57°C for 60 seconds to anneal the mixture, then it was raised to 72°C for 1 minute to extend the hybridized primers, and finally it was raised to 72°C for 5 minutes to complete the amplification in 35 cycles. After that, an agarose gel electrophoresis was performed on the PCR reaction mixture using a 1 kb DNA ladder as a size marker. The sequencing of rRNA genes was done using the dideoxy chain termination method.33 The 16S rRNA gene sequences of the KAU10 isolate were uploaded to NCBI Genbank.

Reactions of resting cells
The isolates were cultured for 48 hours at 30°C in 500 mL flasks with 250 mL AVSG medium containing 100 mg DBT/L. After collecting the cells by centrifugation at 9000 g for 30 minutes at 4°C, they were washed twice in 0.1 m potassium phosphate buffer (pH 7.0) and kept at 20°C. 1 mL of the cell suspension was added to 33mL of 30% (v/v) glycerol and 10 mL of 1% (v/v) DBT in ethanol in a test tube until the final concentration was 6.60 g/L. The resting cell reaction was allowed to continue for 1 hour at 30°C with 150 rev/min of reciprocal shaking.

RESULTS AND DISCUSSION

DBT-supporting microorganisms
10 bacterial representative types that were predominantly growing on BSM medium added with DBT were taken from two different oil-contaminated sites for the current study. The Gibbs test was used to check each of isolates either having 4S pathway metabolic activity or not, and one bacterium (designated as KAU10) isolated from the mix soil of sites 1 and 2 was discovered to be positive for the 4S pathway. The Gibb’s test, which revealed the development of blue color due to produced 2-HBP, the ultimate byproduct of the 4S pathway, validated this.34 The Gibb’s assay was previously used by a number of researchers to assess the desulfurization activity of bacteria via the 4S pathway.35-37 Because of their extensive culture in basal salt medium (BSM) supplemented with glucose as a carbon source and DBT as the only sulfur source, the other isolates in our analysis that tested negative for the Gibb’s assay may be using the Kodama pathway and Van Afferden system to metabolize DBT.

GC-MS to detect 4S pathway’s intermediates and final product
To find the metabolites of the 4S pathway, the Gibb’s test positive bacterial isolate (KAU10) underwent GC-MS analysis. The chemicals with retention times of 11.2 and 8.48 minutes in the KAU10 isolation culture broth were characterized as DBT (parent compound) and the 2-HBP (formed final product), respectively, by GC-MS (Figure 1 and 2). Li et al. used GC-MS to examine DBT cultured media from Mycobacterium sp. X7B and found DBT sulfone and 2-HBP. Using the newly isolated Gordona strain CYKS1 and the GC chromatogram of DBT grown broth, Rhee et al. discovered 2-HBP during DBT desulfurizing research. The significant fragmentation ions at m/z 139 were seen in the DBT mass spectra of the KAU10 isolate, along with a molecular [M+] ion peak at m/z 184. The molecular weight of DBT is represented by this peak. Major metabolite of KAU10 showed a molecular [M+] ion peaks at the molecular mass of (m/z) 141, 139, 115, 102, 89,70, 63 51,39, 27) obtained from the library of GC-MS machine, confirms the metabolite to be 2-HBP which is the end product of 4S pathway from DBT as a parent organosulfur compound. Each molecule has its distinctive breaking patterns by them they are identified. This finding provides strong support for several previous publications.38-40 as seen in Figure 3. However, when Akhtar et al. used GC-MS to examine the mass spectra of DBT culture liquid media of Rhodococcus species, they found that the molecular ion peaks for DBT sulfone and 2-HBP were quite similar. DBT-sulfone was also detected with our culture isolate (data not shown).

Figure 1. Stucture of Dibenzothiphene (DBT)-A and 2-Hydroxy biphenyl-(2-HBP)-B

Figure 2. GC-MS Chromatogram obtained for the bacterial isolate KAU10 from broth extract showing peaks of parent compound, DBT at 11.25 min. and metabolites formed, 2-HBP at 8.48 min

Figure 3. Shows the mass spectrum of 2-HBP metabolite obtained from bacterial isolate KAU10

DBT desulfurizing bacteria’s amplified dsz operon genes
The presence of the dsz ABC operon genes was confirmed by the increased expression of these genes in the bacterial strain KAU10 (Figure 4). It is noteworthy that both isolates contained the dsz operon on their genomic DNA, which is consistent with a previous finding. Shavandi et al. found the dsz operon genes on the chromosome of Gordonia alkanivorans RIPI90A, which are necessary for DBT desulfurization. However, the dsz operon was discovered to be present on plasmid in the Rhodococcus erythropolis IGTS8 model strain used in biodesulfurization studies.

Figure 4. Shows the dsz operon genes of the KAU10 bacterial strain as they appeared on a PCR gel

Figure 5. Colony morphology and DBT clear zone assay (A) and gram stain of KAU10 (B)

The desulfurizing bacteria are Gram positive, filamentous, and provisionally identified as Rhodococcus based on colony characteristics (Table 1 and 2), morphological (shape), clear zone assay, staining (Gram’s and Spore) (Figure 5), and biochemical (citrate utilization test, urea hydrolysis, hydrogen sulfide production, indole test, methyl red, lipid activity, Voges-Proskauer test, and nitrate reduction test) studies. Comparable morphological and biochemical testing allowed Taddei et al. to conclude that Rhodococcus species were the soil bacteria under study. Both bacterial isolates’ 16S rRNA genes were sequenced after being amplified using the common primers. KAU10, a bacterial isolate, has incomplete rRNA gene sequences that were 1,393 bp long. KAU10 and Rhodococcus erythropolis were related to one another, according to the phylogenetic study. Using NCBI’s BLASTn program, it was possible to calculate the species’ percentage of identity. Rhodococcus erythropolis IGTS8 was the source of 99.91% of the identities. Given that the rRNA gene is the oldest, most conserved, and most dispersed portion of the microorganisms’ genomes, it has shown to be a universal tool for phylogenetic analysis and the study of relationships among organisms. Despite the fact that prokaryotes have three distinct ribosomal RNAs-5S, 16S, and 23S only the 16S rRNA sequence is employed since its nucleotides are both evenly sized and simple to sequence. In order to create a phylogenetic tree, the distance-matrix approach is utilized with the rRNA sequence. By logging variations in two or more organisms’ sequences and analysing them using software, the evolutionary distance is calculated. Since there is a chance that the genome has undergone changes that would bring the sequence back to its original state, a statistical correction factor is used. The phylogenetic tree is built following the evolutionary distance measurement. The length of the branches separating the two microorganisms is directly inversely correlated with the differing evolutionary distances of the two species. Phylogenetic trees can be constructed in a variety of ways based on the software/computer application and the number of microorganisms.41

Table (1):
Colony characteristics of the bacterial isolates

Colony Character
KAU10 Isolate
Configuration
Round
Color
White
Elevation
Convex
Size
4.8 mm
Margin
Ciliate

Table (2):
Morphological, Gram staining, Spore shape and Biochemical tests

Characteristics
Bacterial Isolate KAU10
Microscopic observation
Morphological shape
Filamentous
Spore shape
Oval to circular oval
Gram staining
Gram postive
Biochemical Tests
(+/-) / Positive/Negative
Sucrose Test
+
Starch Hydrolysis
+
Catalase test
+
Casein Hydrolysis
+
Oxidase test
+
Citrate utilization test
+
H2S production test
+
Indole test
Lipid Activity
+
Voges-Proskauer test
Methyl red test
+
Nitrate reduction test
+
Urea Hydrolysis
+

Identification of bacteria via the 4S route that have been found to be DBT desulfurization positive
This research confirms that the Rhodococcus erythropolis KAU10 species is an aerobic bacterium that uses the aerobic DBT desulfurization (4S) pathway. Comparing them to microbial strains that display anaerobic biodesulfurization routes, they will be more significant economically and commercially. By processing the oil in an aqueous phase, the water-soluble sulfite that is formed by microorganisms with an oxidative DBT desulfurization route can be easily disposed of. In contrast, the reductive process of anaerobic desulfurization involves the removal of sulfur from DBT as hydrogen sulfide that ultimately leaves sulfur atoms. Desulfurization is possible with anaerobic strains, but the process is laborious, costly, and time consuming to maintain. Additionally, unfavourable compounds can arise from the organic fuel components.35 It is also possible to genetically alter these Rhodococcus erythropolis KAU10 for increased DBT biodesulfurization activity. These genetically enhanced biodesulfurizing Rhodococcus erythropolis KAU10 strains have the potential to be commercially significant and effective when used to desulfurize fuels throughout the procedure used in refineries to make fuels free of sulfur.

Activity of Resting Cells
To ascertain their relative activity, the one strains were put through an identical experiment with the control strain, IGTS8, and the outcomes are displayed in Table 3. R. erythropolis IGTS8 had the second-highest activity level, with 4.36 units, whereas strain KAU10 had a 12.50-unit output. Under the assessed experimental circumstances, all three strains outperformed the control strain. This suggests that the new strains have a good chance of being used as bio-catalysts for oil desulfurization. The almost three fold increase activity is good indication for commercial purposes. This increased activity might be due to better sulfur utilization found in the petroleum contaminated soils in high temperature and high humidity in the area of refinery in Jeddah, Saudi Arabian regions. As soils are highly contaminated with sulfur products. This may be because of better adaptation by KAU10 in such a harsh condition of high temperature and high sulfur contents in the soil.

Table (3):
Specific activity comparison

Strain Cell
Conc.(g/l)
Activity (U)
KAU10
6.6
12.50
R. erythropolis IGTS8
6.6
4.36

1 U = 1 mol 2-HBP/g-cell/h

CONCLUSION

One potential DBT desulfurizing Rhodococcus erythropolis KAU10 species was isolated from oil-contaminated soils near refineries for the current study. The commercial significance of these desulfurizing species is based on their ability to desulfurize DBT found in fuels without destroying the main ring structure of DBT or decreasing the energy content of fuel (mileage), chemical used as a study model for biocatalytic desulfurization via the 4S route. It has been discovered that the dsz operon (A, B, and C) that controls the 4S pathway is present in the Rhodococcus erythropolis KAU10 species. In the biodesulfurization of fuels, this DBT desulfurizing organisms become increasingly important from an ecological and commercial standpoint. This strain is capable of growing on a variety of organosulfur compounds, demonstrating a high and broad range of sulfur compound desulfurization, which is required by the present industrial level of desulfurization. This isolated microbes have more potential for desulfurization than reported previously, hence could be a good option for alternate microbe based sulfur removal from the petroleum products. It has good and promising scope for desulfurization. Its furthur industrial level optimizations are needed to make its use in hydrodesulfurization process and petroleum refineries.

Declarations

ACKNOWLEDGMENTS
The authors would like to thank Department of Biochemistry and DSR King Abdul Aziz University, Jeddah, Kingdom of Saudi Arabia, for the support and facilities provided to carry out the research work.

CONFLICT OF INTEREST
The authors declare that there is no conflict of interest.

AUTHORS’ CONTRIBUTION
AA conceptualized the project and performed the experiments. AA, OAB, MSN and VA wrote, reviewed and edited the manuscript. All authors read and approved the final manuscript for publication.

FUNDING
The Deanship of Scientific Research (DSR) at King Abdul Aziz University, Jeddah, Saudi Arabia, has funded this project under grant no. (G:188-130-1441), which is greatly acknowledged.

DATA AVAILABILITY
All datasets generated or analyzed during this study are included in the manuscript.

ETHICS STATEMENT
Not applicable.

References
  1. Gulf economy News, 2022, Arab daily News April,2022. https://economic-research.bnpparibas.com/pdf/en-US/Gulf-countries-challenge-energy-transition-3/9/2023,48341
  2. Eiichi K, Kohichi S, Masakazu I. Preface – 3rd International Conference on Environmental Catalysis. Applied Catalysis B-environmental – Appl Catal b-Environ. 2003;41:1-1.
    Crossref
  3. Song CS, Ma XL. New design approaches to ultra-clean diesel fuels by deep desulfurization and deep dearomatization. Appl Catalysis B: Environ. 2003;41(1-2):207-238.
    Crossref
  4. Schilling BM, Alvarez LM, Wang DIC, Cooney CL. Continuous desulfurization of dibenzothiophene with Rhodococcus rhodochrous IGTS8 (ATCC 53968). Biotechnol Prog. 2002;18(6):1207-1213.
    Crossref
  5. Xu P, Yu B, Li FL, Cai XF, Ma CQ. Microbial degradation of sulfur, nitrogen and oxygen heterocycles. Trends Microbiol. 2006;14(9):398-405.
    Crossref
  6. Wei D, Liu L, Shi J, Yan W, Chen X, Li X. Biodesulfurization of thiosulfate by a Pseudomonas strain PSP1 and the investigation of underlying metabolic mechanisms. Environ Sci Pollut Res Int. 2022;29(22):33764-33773.
    Crossref
  7. Chen S, Zhao C, Liu Q, Zang M, Liu C, Zhang Y. Thermophilic biodesulfurization and its application in oil desulfurization. Appl Microbiol Biotechnol. 2018;(21):9089-9103.
    Crossref
  8. Feng S, Lin X, Tong Y, Huang X, Yang H. Biodesulfurization of sulfide wastewater or elemental sulfur recovery by isolated Halothiobacillus neapolitanus in an internal airlift loop reactor. Bioresour Technol. 2018;264:244-252.
    Crossref
  9. Peh S, Mu T, Zhong W, et al. Enhanced Biodesulfurization with a Microbubble Strategy in an Airlift Bioreactor with Haloalkaliphilic Bacterium Thioalkalivibrio versutus D306. ACS Omega. 2022;7(18):15518-15528.
    Crossref
  10. Kilbane JJ. Microbial biocatalyst developments to upgrade fossil fuels. Curr Opin Biotechnol. 2006;17(3):305-314.
    Crossref
  11. Lee MK, Senius JD, Grossman MJ. Sulfur-specific microbial desulfurization of sterically hindered analogs of dibenzothiophene. Appl Environ Microbiol. 1995;61(12):4362-4366.
    Crossref
  12. Lichtinger T, Reiss G, Benz R. Biochemical identification and biophysical characterization of a channel-forming protein from Rhodococcus erythropolis. J Bacteriol. 2000;182(3):764-770.
    Crossref
  13. Moniticello DJ. Biodesulfurization and the upgrading of petroleum distillates. Curr Opin Biotechnol. 2000;11(6):540-546.
    Crossref
  14. Oldfield C, Pogrebinsky O, Simmonds J, Olson ES, Kulpa CF. Elucidation of the metabolic pathway for dibenzothiophene desulfurization by Rhodococcus sp. strain IGTS8 (ATCC 53968). Microbiol. 1997;143(Pt 9):2961-2973.
    Crossref
  15. Okada H, Nomura N, Nakahara T, Maruhashi K. Analysis of dibenzothiophene metabolic pathway in Mycobacterium strain G3. J Biosci Bioeng. 2002;93(5):491-497.
    Crossref
  16. Okada, H, Nomura, N, Nakahara, T, Saitoh, K, Uchiyama, H, Maruhashi, K . Analyses of microbial desulfurization reaction of alkylated dibenzothiophenes dissolved in oil phase. Biotechnol Bioeng. 2003;83(4):489-497.
    Crossref
  17. Kalita M, Chutia M, Jha DK, Subrahmanyam G . Mechanistic Understanding of Gordonia sp. in Biodesulfurization of Organosulfur Compounds. Curr Microbiol. 2022;2;79(3):82.
    Crossref
  18. Murarka P, Srivastava P. An improved method for the isolation and identification of unknown proteins that bind to known DNA sequences by affinity capture and mass spectrometry. PLoS One. 2018;23;13(8):e0202602.
    Crossref
  19. Naito M, Kawamoto T, Fujino K, Kobayashi M, Maruhashi K, Tanaka A. Long-term repeated desulfurization by immobilized Rhodococcus erythropolis KA2-5-1 cells. Appl Microbiol Biotechnol. 2001;55(3):374-378.
    Crossref
  20. Rangra S, Kabra M, Gupta V, Srivastava P . Improved conversion of Dibenzothiophene into sulfone by surface display of Dibenzothiophene monooxygenase (DszC) in recombinant Escherichia coli. J Biotechnol. 2018;10:287:59-67.
    Crossref
  21. Adlakha J, Singh P, Ram SK, et al. Optimization of conditions for deep desulfurization of heavy crude oil and hydrodesulfurized diesel by Gordonia sp. IITR100. Fuel. 2016;184:761-769.
    Crossref
  22. Akhtar N, Akhtar K, Ghauri MA. Biodesulfurization of Thiophenic Compounds by a 2-Hydroxybiphenyl-Resistant Gordonia sp. HS126-4N Carrying dszABC Genes. Curr Microbiol. 2018;75(5):597-603.
    Crossref
  23. Abin-Fuentes A, , Daniel MESM, Wang IC, Prathera KLJ. Exploring the Mechanism of Biocatalyst Inhibition in Microbial Desulfurization. Appl Environ Microbiol. 2013;79(24):7807-781724.
    Crossref
  24. Khedkar S, Shanker R. Isolation and classification a soil actinomycete capable of sulphur- specific biotransformation of diebenzothiophene, benzothiophene and thianthrene. J Appl Microbiol. 2014;118(1):62-74.
    Crossref
  25. Kayser KJ, Bielaga-Jones BA, Jackowski K, Odusan O, Kilbane IIJJ. Utilization of organosulphur compounds by axenic and mixed cultures of Rhodococcus rhodochrous IGTS8. J Gen Microbiol. 1993;139(12):3123-3129.
    Crossref
  26. Duarte GF, Rosado AS, Seldin L, Araujo W, Van Elsas JD. Analysis of bacterial community structure in sulfurous-oil-containing soils and detection of species carrying dibenzothiophene desulfurization (dsz) genes. Appl Environ Microbiol. 2001;67(3):1052-1062.
    Crossref
  27. Li GQ, Ma T, Li SS, Li H, Liang FL, Liu RL. Improvement of dibenzothiophene desulfurization activity by removing the gene overlap in the dsz operon. Biosci Biotechnol Biochem.2007;71(4):849-854.
    Crossref
  28. Kim EK, Jang WH, Ko JH, et al. Lipase and its modulator from Pseudomonas sp. strain KFCC 10818: Proline-to glutamine substitution at position 112 induces formation of enzymatically active lipase in the absence of the modulator. J Bacteriol. 2001;183(20):5937-5941.
    Crossref
  29. Reddy NG, Ramakrishna DPN, Raja Gopal SV. A morphological, physiological and biochemical studies of marine Streptomyces rocheri (MTCC 10109) showing antagonistic activity against selective human pathogenic microorganisms. Asian J Biol Sci. 2011;4(1):1-14.
    Crossref
  30. Bennett JA, Kandell GV, Kirk SG, McCormick JR. Visual and microscopic evaluation of Streptomyces developmental mutants. J Vis Exp. 2018;12(139):57373.
    Crossref
  31. Frank JA, Claudia IR, Sharma S, Weisbaum JS, Wilson BA, Olsen GJ. Critical Evaluation of two primers commonly used for amplification of bacterial 16S rRNA genes. Appl Environ Microbiol. 2008;74(8): 2461-2470.
  32. Kumar V, Bharti A, Gusain O, Bhist GS. An improved method for isolation of genomic DNA from filamentous actinomycetes. J Sci Engg Tech Mgt. 2010;2(2):10-13.
  33. Kurnijasanti R, Isnaeni I, Poernomo AT, Sudjarwo SA. Phylogenetic analysis and anti microbial activity of Streptomyces spp. Isolated from compost soil in Surabay Indonesia on the basis of 16S rRNA gene. Folia Medica Indonesiana. 2017;53(3):204-208.
    Crossref
  34. Rahpeyma SS, Mohammadi M, Raheb J. Biodesulfurization by two bacterial strains in cooperation with Fe3O4, ZnO and CuO nanoparticles. J Microb Biochem Technol. 2017;9(2):587-591.
  35. Sadare OO, Obazu F, Rasekh B, Daramola MO. Biodesulfurization of petroleum distillates – Current status, opportunities and future challenges. Environments. 2017;4(4):85.
    Crossref
  36. Shahaby AF, El-din KME. Desulfurization of crude oil and oil products by local isolated bacterial strains. Int J Curr Microbiol App Sci. 2017;6(4):2695-2711.
    Crossref
  37. Li L, Liao Y, Luo Y, et al. Improved efficiency of desulfurization of oil sulfur compounds in Escherichia coli using a combination of desensitization engineering and DszC overexpression. ACS Synth Biol. 2019;8(6):1441-1451.
    Crossref
  38. Mohebali G, Ball AS, Kaytash A, Rasekh B. Dimethy sulfoxide (DMSO) as the sulfur source for the production of desulfurizing resting cells of Gordonia alkanivorans RIPI90A. Microbiol. 2008;154(3):878-885.
    Crossref
  39. Mohammed MES, Yacoub ZHA, Vedakumar JV. Biocatalytic desulfurization of thiophenic compounds and crude oil by newly isolated bacteria. Front Microbiol. 2015;6:112.
    Crossref
  40. Ismail W, El-Sayed WS, Raheem ASA, Mohamed ME, El Nayal AM. Biocatalytic desulfurization capabilities of a mixed culture during non-destructive utilization of recalcitrant organosulfur compounds. Front Microbiol. 2016;7:266.
    Crossref
  41. Chapus C, Dufraigne C, Edwards S, Giron A, Fertil B, Deschavanne P. Exploration of phylogenetic data using a global sequence analysis method. BMC Evol Biol. 2005;5:63.
    Crossref

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