This Methyl tert-butyl ether (MTBE) is one of the main additives in gasoline to increase octane rating and consequently reduce air pollution. The physico-chemical properties of this substance (high water solubility, low sorption in soil) result in high mobility and considerable concentrations in aquifers. In this survey, Isfehan Refinery that was encountered with MTBE contamination problem was selected as a case study and the MTBE degradation ability of this contaminated area by its indigenous microorganisms was investigated. In the first step of this survey, the influence of various factors on the aerobic degradation of MTBE such as mixed culture type, incubation time, microbial culture and optimal concentration of MTBE were investigated in shaking flasks and the most important factors were specified by means of fractional factorial design 1/2. In the second stage by using optimal values which obtained from the first stage, the effects of co-substare parameter and inoculum parameter were assayed by means of response surface method. The results of the experiments showed that the mixed culture type and initial concentration of MTBE were the most significant factors. The results of the experiments showed that the mixed indigenous culture acted better than activated sludge. The initial concentration of MTBE was also one of the most significant factors. At the best condition about 31 percent of MTBE was treated by co-substrating with n-hexane in a ratio of 0.2.
Methyl tert-butyl ether (MTBE), a synthetic compound produced from methanol and isobutylene, has been used as a gasoline additive to increase octane ratings instead of lead-based and aromatic compounds since the late 1970s. For the last 15 years, it has been added in higher concentrations (up to 15% (v/v)) to increase fuel combustion efficiency and to lower emissions of CO and other air pollutants [
There are different technologies that have been applied to remediate groundwater polluted by MTBE and other gasoline compounds such as pump and treat, air sparging, multi-phase extraction, and in-situ chemical oxidation [
Cometabolic MTBE biodegradation has received significant research attention. Cometabolism involves the use of an additional carbon source for growth and may have a role in natural attenuation. Some compounds present in gasoline have been reported for their ability to induce enzymes able to degrade MTBE [
In this study, the aerobic MTBE degrading capacity of the indigenous microbial community in soil from gasoline contaminated sites in Isfehan Refinery, is examined in batch experiments simulating different in-situ conditions.
Soil samples were collected at 5 - 20 cm depth from MTBE contaminated ground surface of Isfehan Refinery. These samples were used for reaching the indigenous microorganisms. Ten grams of soil sample were dissolved in 100 ml sterilized water and shaken at 150 rpm and 30˚C for 3 hrs and then left standing for 30 mins. The supernatant 10 ml was then incubated into 200 ml modified M9 as growth medium with the following formulation: Na2HPO4, 6.0 g/l; KH2PO4, 3.0 g/l; NaCl, 0.5 g/l; NH4Cl, 1.0 g/l; MgSO4.7H2O 1.0 M, 2.0 ml/l; CaCl2 1.0 M, 0.1 ml/l (all chemicals were purchased from Merck). MTBE as the sole carbon and energy source was added to a final concentration of 200 ppm and the mixture was shaken in a 500 ml flask for 24 h at 150 rpm and 30˚C. Subsequently, 20 ml of the inocula (supernatants of the above cultures) was transferred to another 500 ml flask containing 200 ml of modified fresh M9 medium supplemented with MTBE (300 ppm) and was incubated for another 24 hrs under the same conditions. This procedure was repeated over 10 days until the concentration of MTBE reached to 1000 ppm in the last fresh modified M9 medium. After the final transfer, 100 µl of the culture was spread on Nutrient agar medium plates and incubated for 24 hrs at 30˚C. Nutrient agar medium plates were maintained at 4˚C.
In this part of study, feasibility of MTBE bioremediation was assessed by a combined microbial culture that was separated from MTBE contaminated soil. To evaluate this method’s applicability, a series of experiments based on design of experiments by Minitab software were done in which superficial MTBE contaminated water samples were used for preparing the mixed bacterial culture. Experiments were conducted to examine the feasibility of MTBE biodegradation under aerobic and aerobic-cometabolic condition. Experiments were conducted in two stages. At first stage, the effects of mixed culture type, initial concentration of MTBE, incubation time and culture medium type were investigated. All experiments were carried out in sealed 250-mL Erlenmeyer flasks. The flasks contained 90 mL of a culture medium type (M9 or nutrient broth) and MTBE. Based on design table (see
At the second stage (after analyzing the results of stage 1) the effects of inoculum size and the presence of co substrate factors were investigated based on
Minitab 16 was used for designing of experiments and all of statistical analysis. The method for the first stage designing was fractional factorial ½ with resolution of ΙV and for second stage was response surface method (Central Composite Design). ANOVA was used to determine the significance of regression and factors. ANOVA was also used to assess differences between appropriates measured parameters. The first stage design table and the second stage design table are given in
MTBE in groundwater are measured using headspace solvent micro extraction (HSME) method, with gas chromatography-flame ionization (GC-FID). HSME is a novel method of sample preparation for chromatography
No. of Exp. | Factors | MTBE Biological Removal Percent | |||
---|---|---|---|---|---|
Mixed Culture Type | Initial Concentration of MTBE (ppm) | Incubation Time (h) | Culture Medium Type | ||
1 | Indigenous microorganisms | 200 | 24 | M9 | 22.79 |
2 | Indigenous microorganisms | 1000 | 24 | NB | 2.69 |
3 | Indigenous microorganisms | 200 | 120 | NB | 17.80 |
4 | Indigenous microorganisms | 1000 | 120 | M9 | 5.00 |
5 | Activated sludge | 1000 | 24 | M9 | 1.31 |
6 | Activated sludge | 200 | 24 | NB | 2.66 |
7 | Activated sludge | 200 | 120 | M9 | 1.07 |
8 | Activated sludge | 1000 | 120 | NB | 0.30 |
No. of Exp. | MTBE/n-Hexane (w/w) | Inoculum Size (OD) | MTBE Biological Removal Percent |
---|---|---|---|
1 | 0.2 | 0.2 | 30.38 |
2 | 0.2 | 0.4 | 29.76 |
3 | 0.2 | 0.6 | 30.98 |
4 | 0.6 | 0.2 | 25.43 |
5 | 0.6 | 0.4 | 24.95 |
6 | 0.6 | 0.6 | 25.59 |
7 | 1 | 0.2 | 22.38 |
8 | 1 | 0.4 | 22.80 |
9 | 1 | 0.6 | 21.92 |
analysis. This system involves a microdrop of a high boiling point organic solvent (n-decane in this study) extruded from the needle tip of gas chromatographic syringe, which is exposed to the headspace above a sample. Volatile organic compounds (MTBE in this study), are extracted and concentrated in the microdrop. Then, the microdrop is retracted in the microsyringe and injected directly into a chromatograph. The high volatility and low polarity of MTBE lead the compound to have a fast diffusion to headspace and an enhanced distribution into the microdrop, respectively. Theses characteristic leads to study the determination of MTBE in water samples by a HSME method using a GC-FID equipment [
The control samples were prepared for considering MTBE removal by abiotic processes. The percentages of biotic and abiotic removal of MTBE (R%) was obtained by the following equations:
The results of stage one showed that indigenous microorganisms of the region could biodegrade MTBE effectively comparing to activated sludge. Based on the analysis of Minitab software, it was found that out of four main factors, two of them including culture type and initial concentration of MTBE had significant effects on biodegradation of MTBE with p-value < 0.05. In contrast, incubation time and culture medium factors had insignificant effect on MTBE degradation with p-value > 0.05. MTBE disappearance in the all controls was negligible.
Result showed that the indigenous microorganisms capability in MTBE degradation, as predicted, were higher compared to activated sludge. This phenomenon was probably interpreted in order of indigenous microorganisms acclimation with MTBE. According to data from experiments number 1 and 2 and also experiments number 3 and 4 and considering culture medium factor as an insignificant factor (p-value of media culture > 0.05), MTBE degradation percent is decreased when MTBE initial concentration is increased. Similar results are reported in [
Incubation time factor has no significant effect on MTBE degradation (p-value > 0.05). According to data from experiments number 1 and 3 and also 2 and 4 and considering culture medium factor as an insignificant factor, it is found that although MTBE degradation percent is increased with spreading time, this factor has insignificant effect on MTBE degradation percent practically. This could be ascribed to the presence of tert-butyl alcohol (TBA) as an intermediate in the most of MTBE-degrading culture and its inhibitory effect on MTBE degradation so that is suggested that a competition between two components occurred. It can be presumed that the same enzyme possibly responsible for MTBE and TBA metabolism and they may be competing for the same active site [
According to the Minitab software, the medium culture has no significant effect on MTBE degradation. Although both M9 and NB can prepare Nitrogen and Phosphorous supply for microorganisms, MTBE degradation percent in M9, was higher comparison to NB. This can be intrepid by considering MTBE as the sole carbon source in M9.
Microorganism, MTBE initial concentration, incubation time and MTBE biological removal percent for similar studies are presented in
According to results of stage two, the presence of cometabolite has significant effect on MTBE degradation (p-value < 0.05) and MTBE biological removal percent is increased. One potential reason is that some oxidizing enzymes during consumption of n-hexane are produced which promote MTBE removal efficiency. The result indicated that the highest MTBE degradation percent is achieved in MTBE to n-Hexane ratio (w/w) equal to 0.6.
The effect of inoculum size on MTBE biodegradation was tested. According to result of stage two, inoculum size factor had no significant effect on MTBE biodegradation (p-value > 0.05) and no difference was observed with the increasing of inoculum size. Although, inoculum size could play a role in MTBE removal soon after the inoculation, the degradation rate reaches a constant. This interpretation is consistent with findings of Zhang et al. [
The results of this study provide evidence of MTBE degradation by indigenous microorganisms. Aerobic microbial consortia is taken from the groundwater and soil of a contaminated site and enriched, to test whether they are capable of degrading MTBE as sole source of carbon. Current study shows that indigenous microbial populations are able to remove MTBE from aqueous samples. Furthermore, it emerges from the results of this study that when the initial concentration of MTBE is 200 ppm, biological removal of MTBE is enhanced. The results of design of experiments by response surface method show that using of n-hexane as the co metabolite provides a solution to overcome low biodegradation of MTBE.
Microorganisms | Initial MTBE Concentration | Incubation Time | MTBE Removal Percent | Reference |
---|---|---|---|---|
Achromobacter xylosoxidanns MCM1/1 | 100 ppm | 5 d | 78% | [ |
Bacillus Rhodococcus Micrococcus Aureobacterium Proteus | 100 ppm | 5d | 22% - 37% | [ |
Microbial consortium from MTBE contaminated groundwater | 950 ppm | 3d | 25% | [ |
Indigenous microorganisms | 200 ppm | 1d | 23% | Current study |
The authors would like to thank Mr. Damirchi and financial support of Isfahan Petroleum Refinery.
BaharehMontazeri,Mohammad HosseinSarrafzadeh, (2016) Microbial Community from MTBE-Contaminated Soil for Aerobic Biodegradation of MTBE. Journal of Geoscience and Environment Protection,04,93-99. doi: 10.4236/gep.2016.41011