Skip to main content
Advertisement
Browse Subject Areas
?

Click through the PLOS taxonomy to find articles in your field.

For more information about PLOS Subject Areas, click here.

  • Loading metrics

Optimization of Biodesulfurization of sour heavy crude oil

Abstract

Biodesulfurization of fossil fuels is a promising method for treating the sour oil due to its environmental friendliness and ability to get rid of the recalcitrant organosulfur compounds. In this study, many types of microorganisms such as Ralstonia eutropha, Rhodococcus erythropolis, Acidithiobacillus ferrooxidans, and Acidithiobacillus thiooxidans applied on a sour heavy crude oil (sulfur content was 4.4%). Also, a colony isolated from the crude oil and oil concentrate was examined by supplying it with PTCC 106. The various official and famous mediums were significantly evaluated such as (PTCC 2, PTCC 105, PTCC 106 (9K), PTCC 116, PTCC 123, PTCC 132), sulfur-free MG-medium, basal salts medium, and mineral salts. It was found that Rhodococcus erythropolis and Acidithiobacillus ferrooxidans from microorganisms and SFM and the medium PTCC 105 were selected as the higher desulfurization efficiencies of crude oil equaling 47 and 19.74% respectively. The bioreactions depend on the treated fluid, targeting sulfur compounds as these represent the environmental status (amounts and types of nutrients), and the type of biotreaters whether microorganism are septic, semiseptic, or aseptic. The optimum operation conditions have been designed by using Definitive method such as mixing speed, temperature, surfactant dose, OWR, acidity. The optimum efficiencies obtained here are better than the previous efforts even though those gained by bioengineering. Biodesalination was a simultaneous process with the BDS.

Introduction

Fossil Fuel is an important source of energy or power in various fields in life and industry. Before applying it in customization use, it must be on specification of some related standards to avoid risks on HSE. Then, sulfur compounds are one of these constraints to be treated, or else, they formulate a gangerence on quality and HSE limitations heart diseases, asthma, and respiratory illnesses [1].

There are many methods of treatment such as adsorptive desulfurization-adsorption (ADS) [2], microbial and bacterial desulfurization (BDS) [3], Extraction (Desulfurization by Extraction, EDS) [4], ODS-Oxidative Desulfurization (Desulfurization by oxidation DO) [1], supercritical water-based (water) desulfurization (SWD) [5]. Also, a combination is such as BDS-ODS-EDS [6], EDS-HDT [7], OEDS (Oxidation Extraction Desulfurization), microwave catalytic hydrogenation process [6].

BDS is more efficient and less expensive than the remaining methods as HDS in removing sulfur from refractory heterocyclic compounds present in crude oil, it could be used in oil refineries as a complement to achieve ULSD. Indeed, BDS can be used to desulfurize heavy oils, as shale oils, which have high thiophene concentration [8].

Few studies and patents were subjected on a real fractions as the whole crude oil in aerobic or anaerobic conditions by Achromobacter, Leptospirillum, Pseudomonas, Sulfolobus, Thiobacillus, Rhodococcus strains, Sphingomonas subarctica, Bacillus, Desulfovibrio desulfuricans, Pyrococcus, Desulfomicrobium scambium, Desulfovibrio longreachii, Pantoea agglomerans [9,10]. The advantage of BDS of whole crude oil is to reduce the costs of desulfurization treatment in refineries [11]. Also, BDS could be applied on the oil derivatives such as the LPG, petrol (gasoline), jet fuel (Aeroplane), kerosene, fuel oil (heavy oil of furnace or reboiler), and gas oil, and cracked stocks were applied to the BDS by these various microorganisms Mycobacterium goodii, Pseudomonas, Gordonia, Rhodococcus, Mycobacterium phlei, Pseudomonas delafieldii, Paenibacillus, Rhodoccocus globerulus, Nocardia [11,12].

Furthermore, a model compounds can be applied to lump and represent the whole fossil fuel especially the recalcitrant HCS [13] such as BT, DBT, DBTO2,M DBTSO2, MgSO4, BNT, DBS, 2,8 DMDBT, 2,6 DNDBT, DMDBT, thianthrene [8,1423]. Finally, the microorganisms of BDS applied on water or coal could be common in application of oil [24].

Materials and methods

Materials

Nutrient components: There are many chemical components required in the preparation of culture mediums of microorganisms in order to achieve the growth and desulfurization. According to the inventory of recipe of nutrient media in appendix, the chemical species can be divided into carbohydrates, minerals, proteins and vitamins, furthermore, adaptation agents, acids and bases as HCl NaOH, and surfactants (Tween polysorbate 80 C64H124O26 and PEG as emulsification and demulsification reagents respectively [25].

Six official types of mediums were prepared by using the chemical species: medium PTCC 105, medium PTCC 106 (9K), medium PTCC 119, medium PTCC 123, medium PTCC 132, and medium PTCC 69 ‘Nutrient Broth (LB)’. Also, three typical mediums were applied: sulfur free mineral medium SFM [3], basal salt medium (BSM), mineral salt medium (MS). These mediums were prepared for seed culture of the microorganisms.

Then, the applied mediums were as follows (per 1000 ml of distilled water): PTCC 2 (pH 7) “LB, NB”: CaCl2 5 g, peptone 5 g, meat extract 3 g, MnCl2.2H2O 10 mg, CaCl2.2H2O 100 mg, MgSO4.7H2O 500 mg, pH 7; PTCC 105 (pH 1.4) “ferrous sulfate medium Theobacillus ferroxidans medium with ferrus sulfat”: FeSO4 33.33 g, KH2PO4 0.4 g, MgSO4.7H2O 0.4 g, (NH4)2SO4 0.4 g; PTCC 106 (pH 2) “9k medium”: FeSO4.7H2O 45 g, glucose 10 g, (NH4)2SO4 3 g, K2HPO4 0.75 g, MgSO4.7H2O 0.5, KCl 0.1 g, CaNO3 0.01 g; PTCC 116 (pH 7) “Propionibacterium Medium”: elemental sulfur 10 g, KH2PO4 3 g, CaCl2.2H2O 0.14 g, NH4Cl 0.1 g, MgCl2.6H2O 0.1 g; PTCC 123 (pH 3.5) “MS medium”: elemental sulfur 5 g, (NH4)2SO4 2 g, K2HPO4 0.25 g, MgSO4.7H2O 0.25 g, KCl 0.1 g; PTCC 132 (pH 1.8) “Leptospirillum (HH) Medium”: CaCl2.2H2O 147 mg, (NH4)2SO4 132 mg, ZnCl2 68 mg, CaCl2.6H2O 64 mg, MgCl2.2H2O 62 mg, MgCl2.6H2O 53 mg, KH2PO4 27 mg, FeSO4 20 mg.

Also, the following mediums were examined: MG-medium sulfur free mineral medium “SFM” (pH 7): glucose 5 g, NH4Cl 1 g, KH2PO4 2 g, K2HPO4 4 g, MgCl2.6H2O 0.2 g, TES 10 ml; whereas, TES: HCl (10 M) 10 ml, CaCl2.2H2O 2 g, NaCl 1 g, ZnCl2 0.5 g, MnCl2.4H2O 0.5 g, CuCl2.2H2O 0.5 g, FeCl2.4H2O 0.4, Na2WO4.2H2O 0.1 g, Na2MoO3.2H2O 0.05 g [26]; BSM (PH 7) “BSM”: MnSO4.7H2O 2.2 g, KH2PO4 1 g, K2HPO4 1 g, NaNO3 1 g, MgSO4.7H2O 0.5 g, CaCl2.9H2O 0.1 g. TES: ZnSO4.7H2O 2.2 g, MnSO4 2 g, H3BO3 0.4 g, CuSO4 0.26 g, Na2MoO4.4H2O 0.26 g, CaCl2 0.22 g, KI 0.006 g [27]; MS “mineral salts”: Na2HPO4.12H2O 3.57 g, KH2PO4 1.5 g, H3BO3 0.02 g, K2SO4 2.2 g, MnSO4.7H2O 0.3 g, FeSO4 0.1 g, MnSO4.5H2O 0.1 g, ZnSO4.7H2O 0.08 g, CuSO4 0.08, fructose 1.5 g.

In the current work, the microorganisms have been purchased from the Persian collection such as RTCCR 77 A. Ralstonia eutrophic (PTCC 1615), Rhodococcus erythropolis (PTCC 1767), Thiobacillus ferrooxidans (PTCC 1646), Thiobacillus thiooxidans (PTCC 1717). A society of pure cultures or colonies can be made in broth medium or slants. Also, a microorganism colony has been isolated from the Iraqi heavy sour crude oil suplemeted by “9k” medium.

Analysis and treatment methods

The important equipment used in the current study is as shown in these both sections. The main equipment for the treatment of desulfurization were the incubators as shown in table below. Test the content of sulfur before the experiment. Experimentally, types of sulfur compounds in crude oil should be determined as total content or detailed compositions by using X-ray before and after the treatment. Also, some other tests can be done as the density and then calculation of API.

For the incubation purpose, IKA(R) ks 4000i, HYSK Shaking Incubator, SANYO CO2 Incubator compatible with Incubator Shaker. STIK oven was used for the evaporation and purification of sample to prepare it for the final test. Trans Instruments BP 3001 and 3020 were used to measure both pH and electric conductivity (EC). The sterilizer Reuhan Teb was used to sterilize the mediums before inoculation and incubation. The centrifuge Duna Velocity 14 was used in the separation of water oil phases according to ASTM 1796. TSN 6 200 sulfur elemental analyzer (NORDTECH, X-Ray (in Tehran lab) was used to test the total sulfur in the crude oil.

The experimental work was proceeded for all the experiments designed by review-based to determine the significant effect of both microorganisms (microorganisms) and culture chemical medium, or Minitab-based design by Definitive blocks to find the optimum conditions for the best microorganisms. The design of experiments was coupling many types of microorganisms with many probable beneficial mediums. Thiobacillus ferrooxidans was examined with the mediums PTCC 2, 105, 106, 132; Rhodococcus erythropolis was examined with MG-medium (SFM), MS, and BSM; RTCC R77 and YFC were examined with the mediums PTCC 2 and 106 respectively. Pretreated Sample (oil, water, and surfactant) with volume compatible with DoE to be enough in the final tests (2 ml) at least for testing the total sulfur. The compositions were: oil 5 ml, inoculation microorganism seed culture 5 ml, incubation chemical medium 50 ml.

Isolation.

Isolation: Microorganisms colony was isolated from the crude oil by using Medium 106 ‘9k’ (100–150 ml) prepared as three solutions all chemicals without FeSO4, only FeSO4, agar. The source of sulfur was crude oil activated with ore concentrate. The isolated colony biomisture can be named as a yellow form colony.

Emulsification.

The emulsifier here was Tween 80. Few amounts of surfactant can be achieved by adding some Tween with water and use droplets to pick from this diluted Tween. Tween is preferred on SDS due to no sulfur in its structure to avoid the probability of its effect on final reading or results if it does not sediment in centrifuge.

Acidity.

It is preferred to set the pH value before sterilization to simplify procedure and keep or assure sterilized environment and sterilized pins. Maybe, this step requires partitioning of the samples to many Erlenmeyer for simplifying the step. Many adjusters are there such as HCl, H2SO4, H3PO4, and NaOH. That H2SO4 is not preferred to be used because it contains S. Usually HCl was used here.

Sterilization.

Sterilization of chemical mediums and lab tools as the cotton and glasses can be occurred in autoclave. Medium 105 was sterilized in autoclave without FeSO4 avoiding sedimentation. FeSO4 was sterilized alone in an autoclave and then mixed with remaining mixture, or can be added by using a micro-filter (micro syringe) (4 μm). The sterilization conditions were setted as the pressure 15 psi, temperature 120 C for 20 min. In the xase of FeSO4, the temperature was setted as 100 C only for 5 to 10 min to avoid its sedimentation in the culture medium.

Inoculation.

Inoculation for fermentation was about 2 days: Erlenmeyer contains (25–100) ml of inocula. It’s not obligatory that the medium of culture is the same as the medium of fermentation. For adaptation, as mentioned before, some drops or 0.5 ml of crude oil can be added. Time of seed culture inoculation must be the same in all experiments in order to keep constant OD for all, let it (t 2 day). Incubator setting for fermentation inoculation T 30–35 C, speed of rotation 150 rpm, and time 2 day.

Incubation.

This step represents the main BDS reaction. That’s of medium (50 ml) and sample (5 ml) wanted to be treated and inoculated biotreater (microorganisms) (5 ml) about 4% [28].

Separation.

The separation of treated samples (oil/water). That’s of treated sample from the previous mixture using gravity settling (decanter flask for about 20–30 min), chemical solvent or cleaner (reverse emulsifier or demulsifier such as hepate), heating (oven) (T 80 C, t 1 day) in case of gel especially in emulsions samples No. (6, 11, 22) and 20, and/or. Also, the medium after separation may contain some oil which can be separated by centrifugation actually (Sr 1Trpm, t 10 min) or (T 20 C, Sr 78269 g, t 1 h) [28] which may be after heating. Practically and usually, 500 rpm and (t 10 min) can be used mostly to separate most samples.

Results and discussion

In this part of the current study, the results of treatment are run on a lab scale. Whereas the main step is the incubators units. The observations, readings, results, and discussion are monitored and tested during the time periods of three days in order to see the profile changes.

Results

The results cab be noted as the isolates, desulfurization, and checking the presence or absence of BDG simultaneously with the BDS of crude oil.

Biopreparation by isolation of yellow form colony.

A yellow bacteria colony, as shown in (Fig 1), was isolated from the crude oil by applying PTCC 106 ‘9k’ medium supplemented by nutrient agar (1.5%) in incubation temperature 35 C for 3 day. The generated isolate was named as the yellow form colony (YFC).

thumbnail
Fig 1. Photograph for the yellow form colony isolated from the crude oil supplemented by 9k medium.

Also, in order to study the septic effect of bacillus strains as known colony, a biomixture of known bacteria (Acidithiobacillus ferrooxidans and Acidithiobacillus thioxidans) was made.

https://doi.org/10.1371/journal.pone.0283285.g001

Significance of Biodesulfurization of crude oil.

In this biotreatment, the results of 13 experiments were found. The following Table 1 shows these observations, readings, and results according to time of inoculation and incubation were 2 and 3 day respectively, as shown in Table 1 and (Fig 2).

thumbnail
Fig 2. Effect of microorganism treaters and environmental mediums on the BDS of whole sour heavy crude oil.

(A) Initial content, (B) Acidothiobacillus ferrooxidans, (C) Acidothiobacillus thioxidans, (D) Rhodococcus erythropolis, (E) Ralstonia eutropha RTCC 77, (F) biomixture (B+C), (G) Isolated colony (yellow form colony).

https://doi.org/10.1371/journal.pone.0283285.g002

thumbnail
Table 1. The efficiencies of both microorganisms and environmental mediums on the BDS of whole sour heavy crude oil.

https://doi.org/10.1371/journal.pone.0283285.t001

Whereas, the efficiency is defined as the change in sulfur content divided by the initial sulfur content.

Checking Uni-objective.

The BDS without BDG was checked for the treated samples by using GC-FID. Whereas the similarity among the samples before and after treatment proved that BDS was not accompanied by BDG or reducing the caloric energy of hydrocarbons. Fig 3 shows that similarity.

thumbnail
Fig 3. Compositions analysis for oil samples.

(A) untreated oil, (B) treated crude oil by Rhodococcus erythropolis IGTS8, and (C) Thiobacillus ferroxidans.

https://doi.org/10.1371/journal.pone.0283285.g003

Optimization of BDS operation conditions.

The experiments have benn designed by Definitive method as shown in the following Table 2. The final sulfur content of crude oil have been found by measuring the total sulfur by ASTM D4294 as shown in the following Table 2.

thumbnail
Table 2. Design of experiment by Definitive method and results by both Rhodococcus erythropolis IGTS8 and Thiobacillus ferroxidans.

https://doi.org/10.1371/journal.pone.0283285.t002

Discussion and analysis

Explanation of Phenotypic Appearance of isolated colony.

Mostly the colony growing on Fe2SO4 medium contained the microorganisms preferring sulfuric mediums such as the Acidithiobacillus ferrooxidans. Therefore, the color is close to the yellow because the celluar morphology is affected with that medium.

BDS efficiency and effect of weight ratio of sources of energy/N/P/Mg.

It was found that the efficiency was related to the type of microorganism, biopurity status (septic, semiseptic, or aseptic), and the enviromental status (amounts and types of nutrients). Table 1 shows the results of significant study of microorganism effect on the desulfurization of crude oil. The most efficient microorganism and mediums were Thiobacillus ferroxidans with PTCC 105, Thiobacillus thiooxidans with PTCC 119, known mixed colony with PTCC 106, Rhodoococcus erythropolis with MG-medium (SFM). It was found that the ThF prefers a minimized ratio of E/N/P as shown in the table. The specificity of Thiobacillus ferroxidans toward the source of energy is the most important and has the highest effectiveness than other sources of N, P, and Mg.

It was found that the pure microorganisms can be developed by adding other microorganisms as in the case of Thiobacillus ferrooxidans and Thiobacillus thiooxidans. The biomixtiture is rather to be with regarding the preferred medium for each microorganism due to the pur Thiobacillus ferrooxidans with PTCC 105 achieved desulfurization more than both of the Thiobacillus thiooxidans and the relative colony.

While, the isolated colony is not purified, therefore, this leads to a lower efficiency of BDS, because it was applied in septic conditions.

When the microorganism Rhodococcus erythropolis was applied, the mediums effect ranked according to this series SFM, MS, NB, and BSM respectively. The medium free of sulfur (or medium whose difficulty in withdrawal of sulfur) with oil in treatment led to finding microorganisms working on dissociation of C-S bonds in crude oil and necessity of presence of crude oil for adaptation in seed culture, fermentation, main treatment of incubation.

The differentiation of efficiencies in desulfurization of crude oil can be significantly due to the differences in the ratio of sources of C/N/P affecting the growth and treatment of Rhodococcus erythropolis, i.e., the ratio among the carbohydrates/nitrates/phosphates in Rhodococcus strain [29], whereas, its 5/1/6 in SFM, while 1.5/0/5 in MS, and 0.1/1/1/0.5 in BSM as shown in Table 2. or generally in the various strains [30] and the cell volume [31].

Also, the efficiency varies due to the specificity of microorganisms according to the various types of HCS in the crude oil submitted to the biotreatment. Whereas Rhodococcus erythropolis IGTS8 has a tendency of specificity towards DBT more than alkylated forms and BT respectively, Also, each microorganism has special selectivity for which sources of sulfur [22,32,33]. Also, the various availability of sources of sulfur compounds generate a competitive in desulfurization, therefore the efficiency with multiple substrates is less than single substrate [10,26,34]. Therefore, the microorganisms desulfurize crude oil and its derivative with different efficiencies according to the presence of these HCS in fractions [32].

In general, the pure rate of BDS is low, therefore electrokinetic or sonochemical fields can be used to increase the bioreaction rate [15].

The operation conditions can be seen from the Table 2 to select the optimum conditions which give the highr desulfurization ability.

Checking objective unity, modeling, analysis and optimization.

This showed that those microorganisms preferred the mechanism such as the 4S pathway rather than the destructive pathways [35,36]. This leads towards the BDS kinetic model, away from the BDG models such as Kodami model. The real model of our system is multiple metabolic-based models, for simplification, a single model can be seen here [37]. The following Fig 4 shows comparative pathways between the BDS vs BDG for a model compound represented by DBT.

thumbnail
Fig 4. Metabolism pathways.

(A) Biodesulfurization versus (B) biodegradation pathways.

https://doi.org/10.1371/journal.pone.0283285.g004

The optimum conditions can be found by applying the Minitab- RSM as following Fig 5. The optimal efficiencies were 100% and 99.98% for Rhodococcus erythropolis IGTS8 and Acidithiobacillus ferrooxidans respectively. These results are the best co mparative to the previous efforts in BDS of fuels even those containing deep biological internals [17,38].

thumbnail
Fig 5. Response analysis and optimization of the operating conditions.

(A) Rhodococcus erythropolis IGTS8 and (B) Acidothiobacillus ferroxidans.

https://doi.org/10.1371/journal.pone.0283285.g005

Conclusions

The microorganisms have significant effect differences as biotreaters in the BDS treatment, whereas, the best efficiencies have been gotten by Rhodococcus erythropolis and Thiobacillus ferrooxidans in SFM and medium 105 with desulfurization efficiencies 19.74% and 47% respectively during 3 days in the primary stage. The microorganisms have no significant effect as biotreaters in the BDS treatment were RTCCR 77 A. eutrophic, and the yellow form colony (YFC) with desulfurization efficiencies less than 4% for both of them. Also, the rank of achievement of required objective was found as follows: Rhodococcus erythropolis, Thiobacillus ferrooxidans, RTCCR 77 A. eutrophic, and yellow form colony (YFC). The optimum ranges of operation conditions have been limited by using Definitive method and the optimum values can be found be using the response surface method.

References

  1. 1. Sadare Olawumi O.; Obazu Franklin and Daramola Michael Olawale “Biodesulfurization of Petroleum Distillates—CurrentStatus, Opportunities and Future Challenges” Environments 2017, 4, 85.
  2. 2. Mujahid A, Maryam A, Afzal A, Bajwa SZ, Hussain T, Din MI, et al. Molecularly imprinted poly (methyl methacrylate)-nickel sulfide hybrid membranes for adsorptive desulfurization of dibenzothiophene. Separation and Purification Technology. 2020 Apr 15;237:116453.
  3. 3. Chen S, Zhao C, Liu Q, Zhang X, Sun S, Zang M. Biodesulfurization of diesel oil in oil–water two phase reaction system by Gordonia sp. SC-10. Biotechnology letters. 2019 May 1;41:547–54. pmid:30915612
  4. 4. Abro R, Abdeltawab AA, Al-Deyab SS, Yu G, Qazi AB, Gao S, Chen X. A review of extractive desulfurization of fuel oils using ionic liquids. Rsc Advances. 2014;4(67):35302–17.
  5. 5. Siddiqui SU, Ahmed K. METHODS FOR DESULFURIZATION OF CRUDE OIL-A REVIEW. Science International. 2016 Mar 1;28(2).
  6. 6. Duissenov D. Production and processing of sour crude and natural gas-challenges due to increasing stringent regulations (Master’s thesis, Institutt for petroleumsteknologi og anvendt geofysikk).
  7. 7. Hamad EZ, Al-Shafei EN, Al-Qahtani AS, inventors; Saudi Arabian Oil Co, assignee. Desulfurization of whole crude oil by solvent extraction and hydrotreating. United States patent US 8,343,336. 2013 Jan 1.
  8. 8. Pacheco M, Paixao SM, Silva TP, Alves L. On the road to cost-effective fossil fuel desulfurization by Gordonia alkanivorans strain 1B. RSC advances. 2019;9(44):25405–13. pmid:35530089
  9. 9. Gunam IB, Yamamura K, Sujaya IN, Antara NS, Aryanta WR, Tanaka M, et al. Biodesulfurization of dibenzothiophene and its derivatives using resting and immobilized cells of Sphingomonas subarctica T7b. Journal of Microbiology and Biotechnology. 2013;23(4):473–82. pmid:23568201
  10. 10. Kirkwood KM, Foght JM, Gray MR. Selectivity among organic sulfur compounds in one-and two-liquid-phase cultures of Rhodococcus sp. strain JVH1. Biodegradation. 2007 Aug;18:473–80. pmid:17091345
  11. 11. El-Gendy NS, Nassar HM. Biodesulfurization in petroleum refining. John Wiley & Sons; 2018 Oct 2.
  12. 12. Nassar HN, Abu Amr SS, El-Gendy NS. Biodesulfurization of refractory sulfur compounds in petro-diesel by a novel hydrocarbon tolerable strain Paenibacillus glucanolyticus HN4. Environmental Science and Pollution Research. 2021 Feb;28:8102–16. pmid:33048293
  13. 13. Mohebali G, Ball AS. Biodesulfurization of diesel fuels–past, present and future perspectives. International Biodeterioration & Biodegradation. 2016 May 1;110:163–80.
  14. 14. Alves L, Paixão SM, Pacheco R, Ferreira AF, Silva CM. Biodesulphurization of fossil fuels: energy, emissions and cost analysis. RSC Advances. 2015;5(43):34047–57.
  15. 15. Boshagh F, Mokhtarani B, Mortaheb HR. Effect of electrokinetics on biodesulfurization of the model oil by Rhodococcus erythropolis PTCC1767 and Bacillus subtilis DSMZ 3256. Journal of hazardous materials. 2014 Sep 15;280:781–7. pmid:25244073
  16. 16. Ismail W, El-Sayed WS, Abdul Raheem AS, Mohamed ME, El Nayal AM. Biocatalytic desulfurization capabilities of a mixed culture during non-destructive utilization of recalcitrant organosulfur compounds. Frontiers in Microbiology. 2016 Mar 3;7:266. pmid:26973637
  17. 17. Karimi E, Jeffryes C, Yazdian F, Akhavan Sepahi A, Hatamian A, Rasekh B, et al. DBT desulfurization by decorating Rhodococcus erythropolis IGTS8 using magnetic Fe3O4 nanoparticles in a bioreactor. Engineering in Life Sciences. 2017 May;17(5):528–35. pmid:32624797
  18. 18. Martinez I, Santos VE, Alcon A, Garcia-Ochoa F. Enhancement of the biodesulfurization capacity of Pseudomonas putida CECT5279 by co-substrate addition. Process Biochemistry. 2015 Jan 1;50(1):119–24.
  19. 19. Martínez I, Mohamed ME, Rozas D, García JL, Díaz E. Engineering synthetic bacterial consortia for enhanced desulfurization and revalorization of oil sulfur compounds. Metabolic engineering. 2016 May 1;35:46–54. pmid:26802977
  20. 20. Li L, Liao Y, Luo Y, Zhang G, Liao X, Zhang W, et al. Improved efficiency of the desulfurization of oil sulfur compounds in Escherichia coli using a combination of desensitization engineering and DszC overexpression. ACS Synthetic Biology. 2019 May 27;8(6):1441–51. pmid:31132321
  21. 21. Dejaloud A, Vahabzadeh F, Habibi A. Ralstonia eutropha as a biocatalyst for desulfurization of dibenzothiophene. Bioprocess and biosystems engineering. 2017 Jul;40:969–80. pmid:28341912
  22. 22. Awadh M, Mahmoud H, Abed RM, El Nayal AM, Abotalib N, Ismail W. Diesel-born organosulfur compounds stimulate community re-structuring in a diesel-biodesulfurizing consortium. Biotechnology Reports. 2020 Dec 1;28:e00572. pmid:33365264
  23. 23. Yi Z, Ma X, Song J, Yang X, Tang Q. Investigations in enhancement biodesulfurization of model compounds by ultrasound pre-oxidation. Ultrasonics Sonochemistry. 2019 Jun 1;54:110–20. pmid:30827908
  24. 24. Feng S, Lin X, Tong Y, Huang X, Yang H. Biodesulfurization of sulfide wastewater for elemental sulfur recovery by isolated Halothiobacillus neapolitanus in an internal airlift loop reactor. Bioresource technology. 2018 Sep 1;264:244–52. pmid:29843112
  25. 25. Roodbari NH, Badiei A, Soleimani E, Khaniani Y. Tweens demulsification effects on heavy crude oil/water emulsion. Arabian Journal of Chemistry. 2016 Sep 1;9:S806–11.
  26. 26. Kirimura K, Furuya T, Sato R, Ishii Y, Kino K, Usami S. Biodesulfurization of naphthothiophene and benzothiophene through selective cleavage of carbon-sulfur bonds by Rhodococcus sp. strain WU-K2R. Applied and Environmental Microbiology. 2002 Aug;68(8):3867–72. pmid:12147483
  27. 27. Ohhata N, Yoshida N, Egami H, Katsuragi T, Tani Y, Takagi H. An extremely oligotrophic bacterium, Rhodococcus erythropolis N9T-4, isolated from crude oil. Journal of bacteriology. 2007 Oct 1;189(19):6824–31. pmid:17675378
  28. 28. Chen S, Sun S, Zhao C, Liu Q, Zang M. Biodesulfurization of model oil using growing cells of Gordonia sp. SC-10. Petroleum Science and Technology. 2019 Apr 18;37(8):907–12.
  29. 29. Vrede T. Elemental composition (C: N: P) and growth rates of bacteria and Rhodomonas grazed by Daphnia. Journal of plankton research. 1998 Jan 1;20(3):455–70.
  30. 30. Spaargaren DH. The design of culture media based on the elemental composition of biological material. Journal of biotechnology. 1996 Feb 28;45(2):97–102.
  31. 31. Vrede K, Heldal M, Norland S, Bratbak G. Elemental composition (C, N, P) and cell volume of exponentially growing and nutrient-limited bacterioplankton. Applied and Environmental Microbiology. 2002 Jun;68(6):2965–71. pmid:12039756
  32. 32. Bhatia S, Sharma DK. Biodesulfurization of dibenzothiophene, its alkylated derivatives and crude oil by a newly isolated strain Pantoea agglomerans D23W3. Biochemical Engineering Journal. 2010 Jul 15;50(3):104–9.
  33. 33. Chauhan AK, Ahmad A, Singh SP, Kumar A. Biodesulfurization of benzonaphthothiophene by an isolated Gordonia sp. IITR100. International Biodeterioration & Biodegradation. 2015 Oct 1;104:105–11.
  34. 34. Gunam IB, Sone T, Asano K. Biodesulfurization of the mixture of dibenzothiophene and its alkylated derivatives by Sphingomonas subarctica T7b. Indonesian Journal of Biotechnology. 2021;26(3):122–7.
  35. 35. Ma T. The desulfurization pathway in Rhodococcus. Biology of Rhodococcus. 2010:207–30.
  36. 36. Adlakha J, Singh P, Ram SK, Kumar M, Singh MP, Singh D, et al. Optimization of conditions for deep desulfurization of heavy crude oil and hydrodesulfurized diesel by Gordonia sp. IITR100. Fuel. 2016 Nov 15;184:761–9.
  37. 37. Malani RS, Batghare AH, Bhasarkar JB, Moholkar VS. Kinetic modelling and process engineering aspects of biodesulfurization of liquid fuels: Review and analysis. Bioresource Technology Reports. 2021 Jun 1;14:100668.
  38. 38. Sousa SF, Sousa JF, Barbosa AC, Ferreira CE, Neves RP, Ribeiro AJ, et al. Improving the biodesulfurization of crude oil and derivatives: a qm/mm investigation of the catalytic mechanism of NADH-FMN oxidoreductase (DszD). The Journal of Physical Chemistry A. 2016 Jul 14;120(27):5300–6. pmid:27128525