Abstract
The unique diversity of microbes makes them ideal for biotechnological purposes. In this present study, 16 actinobacterial isolates were screened on media supplemented with Bisphenol A (BPA). Three out of 16 isolates exhibited high biocapacity to degrade BPA as a carbon source. Four different mixed actinobacterial consortia were developed using the above strains and the effect of each consortium on biomass growth; laccase production and BPA degradation were examined. At 100-mg/L BPA concentration, the three-member consortium grew well with maximum laccase activity as well as maximal degradation rate of Bisphenol A than the other two-member consortium. The consortium of Actinomyces naeslundii, Actinomyces bovis, and Actinomyces israelii degraded 93.1% with maximum laccase activity of 15.9 U/mL, followed by A. naeslundii and A. israelii with 87.3% and 9.5 U/mL. This was followed by A. naeslundi and A. bovis with 80.4% and 8.7 U/mL, while A. bovis and A. israelii degraded 76.0% with laccase activity of 7.0. The gas chromatography–mass spectrometry (GC–MS) analysis of biodegraded BPA showed the presence of oxalic acid and new products like 1,2,4-trimethylbenzene and 2,9-dimethyldecane.
Keywords
- Bisphenol A
- laccase
- biodegradation
- biocapacity
- gas chromatography–mass spectrometry (GC–MS)
- Actinomyces naeslundii
- Actinomyces bovis
- Actinomyces israelii
1. Introduction
One of the most pressing health and environmental issues in today’s world is the generation of cumbersome waste with toxic organic substances like Bisphenol A (BPA) from home and industrial sector. BPA poses threats to both aquatic and terrestrial animals [1, 2]. BPA (4,4-isopropylidenediphenol) is an industrial chemical that is produced through the condensation of acetone and phenol using acid or alkaline as catalyst [3, 4].
It is one of the highest production volume chemicals [5], which is widely used as an intermediate in the synthesis of polycarbonate plastics, epoxy resins, and flame retardants [6, 7]. BPA is a monomer of polycarbonate plastics and a constituent of epoxy and polystyrene resins, which are used in the food packing industry [6, 8]. Despite these relevant usages, it has a strong estrogenic property, thus, classified as part of endocrine disruptive compounds (EDCs) [9].
The intensification of anthropogenic activities in manufacturing industries has contributed to the direct or indirect release of a wide range of toxic compounds into the environment and BPA has the potential of causing significant threats to flora, fauna, and human [1, 10, 11]. Microbial degradation is described as a major approach and a natural mechanism, by which one-can clean-up pollutants from the environment in an eco-friendly manner [12, 13, 14].
Most of the exploited biodegradation research processes rely mostly on enzymes from different strain of plankton, fungi, or bacteria [15, 16, 17, 18]. It has been reported that BPA bioremediation by fungi and bacteria is mediated mainly through lignin-degrading enzymes, such as laccase and manganese peroxidase (MnP), which are produced extracellularly [19, 20, 21]. At present, actinobacteria are relatively less explored for biodegradation processes that utilize laccase for remediating BPA.
Laccase is a multicopper oxidase and catalyzes one-electron oxidation of phenolic compounds by reducing oxygen to water [22, 23]. Laccase typically contains 15–30% carbohydrate. It usually has an acidic isoelectric point and a molecular mass of 60–90 kDa [24, 25, 26]. Laccase is encoded by a family of genes and produced in the form of multiple isozymes [27, 28]. It has been proven that genes encoding laccase isozymes were differentially regulated [29, 30].
Laccase is an important industrial enzyme. It can be applied extensively in many fields, which include textile dye transformation, waste detoxification and demineralization, and production of biofuels [31, 32, 33]. In the case of laccase, BPA metabolism is faster in the presence of mediators such as 1-hydroxybenxotriaxzole (HBT) and 2,2-azino-bis (3-ethylbenzthiazoline-6-sulfonate) than in laccase alone. Thus, the objective of this research work was to investigate the microbial growth and laccase activity from the different actinobacterial consortium during the biodegradation process. The metabolites from the BPA biodegradation were also analyzed using gas chromatography–mass spectrometry (GC–MS).
2. Material and methods
2.1 Chemicals and reagents
BPA, hydrochloric acid, sodium acetate, sodium hydroxide, calcium chloride, iron sulphate, potassium phosphate, hydrogen peroxide, ammonium nitrate, and 2,2′azino-di-(3 ~ ethyl benzothiazoline-6-sulphonic acid) (ABTS) were products of Sigma-Aldrich, Germany. Ethanol and yeast extract were ordered from BDH Chemicals Limited, England, Scharlaun Chemie S.A. Barcelona, Spain, and Biomark Laboratories Pune, India. All the other chemicals and reagents used were of analytical grade.
2.2 Microorganism
Sixteen actinobacterial isolates that were obtained from the culture collection of the Enzyme and Microbial Technology laboratory, Department of Biochemistry, Federal University of Technology, Akure, Nigeria, were screening for this study. Three (
2.2.1 Seed culture preparation
Seed culture for each actinobacterial strain was prepared by growing a loopful portion from the slant in sterile media containing (5 g/L), yeast extract (1.5 g/L), beef extract (1.5 g/L), and NaCl (5 g/L) with pH adjusted to 7.4. The media were incubated in an orbital incubator at 30°C for 24 h at 160 r⋅min−1 in a shaking incubator (Stuart, UK). After 24 h, the seed culture was used as inoculum for the production media. Each seed inoculum (constituting 5% v/v) was transferred into 500-mL Erlenmeyer flask containing 100 mL of production media. Three different actinobacterial consortia were developed as follows:
2.2.2 Preparation of mineral salt medium
The mineral salt medium used in this study was composed of KH2PO4 (0.2 g/L), K2HPO4 (0.2 g/L), CaCl2.H2O (0.1 g/L), NaCl (0.8 g/L), MgSO4.7H2O (0.2 g/L), MnSO4.7H2O (0.01 g/L), FeSO4.7H2O (0.02 g/L), and yeast (2.0 g/L) with pH adjusted to 7.0. The basal mineral media was supplemented with 100 mg/L of BPA. These were sterilized in an autoclave at 15 psi and (121°C) for 20 minutes.
2.2.3 Actinobacterial growth during the biodegradation process
Biomass concentration was estimated at every 24 h from the absorbance of appropriately diluted culture medium at 620 nm according to the predetermined correlation between optical density and dry weight of biomass [34, 35]. The media were incubated at room temperature for 312 h at 160 r⋅min−1.
2.3 Effect of actinobacterial consortium on laccase production and BPA degradation
The effect of actinobacterial consortium on laccase production and BPA degradation was investigated for a period of 312 h in sterilized mineral salt media supplemented with 100 mg/L of BPA at pH 7.0. The consortia were developed using equal volume of individual seed culture. BPA degradation efficiency and laccase production were monitored, as described below, at 24-h interval throughout the incubation period.
2.3.1 Enzyme assays
The activity of laccase was measured using the common substrate, ABTS (
At an interval of 1 minute for 5 minutes, the absorbance of the mixture was measured. One unit of laccase activity was defined as the amount of enzyme that oxidized 1 mM of ABTS per minute under standard assay conditions. Laccase activity was expressed as U/mL. The enzyme activity was calculated using the Eq. (1).
2.3.2 Determination of BPA degradation
The percentage removal of BPA was determined using Folin–Ciocalteu reagent according to the method of Yordanova
2.4 Gas chromatography: mass spectrometry (GC: MS) analysis of BPA degradation metabolites
From the quantitative confirmation analysis employing a Shimadzu gas chromatograph GC-2010 series connected to a Shimadzu spectrometer GCMS-QP2010 PLUS (Japan), the separation of the compounds was achieved by employing a DB5MS capillary column (60 m) (Supelco), the carrier gas was helium and maintained at constant flow of (0.9 mL⋅min−1). A sample volume of 1 μL was injected in the splitless mode at an inlet temperature of 280°C. The MS transfer line temperature was maintained at 280°C, whereas the ion source temperature was 180°C.
3. Results and discussion
3.1 Actinobacterial growth
Of all the six actinobaterial isolates examined, only three display the potential to grow on BPA. All the three actinobacterial isolates (
3.2 Influence of consortium on enzyme production and BPA degradation
3.2.1 Effect of consortium on laccase production
The influence of actinobacterial consortium on the production of laccase was studied over the degradation period of 312 h, as shown in Figure 1. The consortium of
3.2.2 Effect of consortium on BPA degradation
The influence of the actinobacterial consortium on BPA degradation was studied over the degradation period of 312 h, as shown in Figure 2. The consortium of
3.3 Degradation by-product of BPA
The mineral-salt-medium-supplemented BPA as a sole carbon source at pH 7.0 inoculated in each actinobacterial consortium was analyzed after an incubation period of 312 h. Cultures were extracted for GC–MS analysis to determine the biodegradation products of BPA. The by-products of BPA degradation were investigated, and each metabolite produced during the biodegradation process is shown in Figure 3. The GC–MS analysis showed that the metabolites could be identified as concerned compounds by comparisons with known authentic compounds using the NIST Chemistry library. The mass peak is found at 38 for 1,2,4-trimethylbenzene, and its relative molecular mass is 120 at the retention time of 4.0 min, while the base peak value was observed at 105. In addition, 2,9-dimethyldecane was identified at mass peak of 21 at the retention time of 4.9 min. The relative molecular mass of the compound 2,9-dimethyldecane was observed as 170 and base peak was noticed at 43. Oxalic acid was also identified as one of the intermediate products, the relative molecular mass of the compound was 216 with a retention time of 7.0 min, and the mass and base peak values were recorded at 12 and 57, respectively. According to Kusvuran and Yildrim [40], oxalic acid was identified as organic intermediate from the degradation of BPA, which is similar to our observation in this study. However, intermediates such as p-hydroxyacetophone, hydroquinone, p-hydroxybenzaldehyde, and p-hydroxbenzoic identified by previous studies [41] were not detected.
4. Conclusion
This study focused on the actinobacterial isolates identified as
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