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Article

Isolation and Optimization of Culture Conditions of a Bioflocculant-Producing Fungi from Kombucha Tea SCOBY

by
Phakamani H. Tsilo
1,*,
Albertus K. Basson
1,
Zuzingcebo G. Ntombela
1,
Tsolanku S. Maliehe
1 and
Rajasekhar V. S. R. Pullabhotla
2
1
Department of Biochemistry and Microbiology, Faculty of Science, Agriculture and Engineering, University of Zululand, P/Bag X1001, KwaDlangezwa 3886, South Africa
2
Department of Chemistry, Faculty of Science, Agriculture and Engineering, University of Zululand, P/Bag X1001, KwaDlangezwa 3886, South Africa
*
Author to whom correspondence should be addressed.
Microbiol. Res. 2021, 12(4), 950-966; https://doi.org/10.3390/microbiolres12040070
Submission received: 25 October 2021 / Revised: 17 November 2021 / Accepted: 21 November 2021 / Published: 14 December 2021
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Abstract

:
Biolocculants are gaining attention in research due to their environmental friendliness and innocuousness to human in comparison to the conventional flocculants. The present study aimed to investigate the ability of fungi from Kombucha tea SCOBY to produce effective bioflocculant in bulk. A 16S rRNA gene sequence analysis was utilized to identify the isolate. The medium composition (carbon and nitrogen sources) and culture conditions (inoculum size, temperature, shaking speed, pH, and time) were optimized using one-factor-at-a-time method. The functional groups, morphology, and crystallinity of the bioflocculant were evaluated using Fourier transform infrared (FT-IR), scan electron microscope (SEM) and X-ray diffractometry (XRD). The fungus was found to be Pichia kudriavzevii MH545928.1. It produced a bioflocculant with flocculating activity of 99.1% under optimum conditions; 1% (v/v) inoculum size, glucose and peptone as nutrient sources, 35 °C, pH 7 and the shaking speed of 140 rpm for 60 h. A cumulus-like structure was revealed by SEM; FT-IR displayed the presence of hydroxyl, carboxyl, amine, and thiocynates. The XRD analysis demonstrated the bioflocculant to have big particles with diffraction peaks at 10° and 40° indicating its crystallinity. Based on the obtained results, P. kudriavzevii MH545928.1 has potential industrial applicability as a bioflocculant producer.

1. Introduction

Flocculation is a purification technique whereby destabilized colloids in solution aggregate together through mechanisms such as charge neutralization and bridging [1]. Flocculants enhance agglomeration of colloidal particles in solution, consequently leading to easy separation [2]. Thus, flocculants are generally used in separation techniques, such as wastewater treatment, drinking water purification, activated sludge dehydration, food fermentation, and downstream processing [3]. They are typically categorized into two groups: chemical and natural flocculants–bioflocculants. Chemical flocculants are further divided into two group namely synthetic organic flocculants, e.g., polyethyleneimine and polyacrylamide byproducts and inorganic flocculants, which include aluminum sulfate and polyaluminum chloride [4]. Chemical flocculants are predominately employed because of their profound effectiveness [5]. However, they can cause harmful effects to humans as they are mutagenic, neurotoxic, and carcinogenic [6]. Moreover, due to their non-degradable nature, they tend to form large volume of sludge, consequently generating environmental pollution [7]. They tend to accumulate in water bodies where fish assimilate them. The assimilated polymers then interfere with fish gill function, causing high fish mortality; consequently leading to reduction in the supply of healthy fish for consumption [8]. Recently, the focus has shifted to the production of natural flocculants, also known as bioflocculants, due to their effectiveness and non-detrimental effects in comparison to chemical flocculants.
Bioflocculants are naturally occurring extracellular biopolymers that result from the exudation of plants and microorganisms including fungi, bacteria, algae, and yeast [9]. In contrast to chemical flocculants, bioflocculants are reported to be environmentally friendly as they are biodegradable and harmless to humans. Moreover, they do not cause any secondary pollution [3]. Louis Pasteur was the first to evaluate the potentiality of bioflocculants produced by the yeast Luvure casseeuse [10]. However, until now, there is a limited number of studies on fungal bioflocculants in comparison to bacterial bioflocculants reported [11]. Nevertheless, microorganisms turn to produce low bioflocculant yields. This has become one of the main constraints for their production and use industrially [12]. Thus, there is a constant search for novel bioflocculant producing strains with capability to produce high bioflocculant yield and enhanced activity [12].
Bioflocculant producing microorganisms have been isolated from a variety of sources, such as soil, palm mill effluents, activated sludge, etc. [13]. However, there are no reports on the isolation of these microorganisms from food such as Kombucha tea SCOBY (symbiotic culture of bacteria and yeast). Kombucha tea SCOBY is a fermented beverage that has recently attracted market attention. The consumption of this tea has expanded from China to all parts of the world due to its health-promoting benefits such as the ability to treat the digestive disorders, stimulate immune system, and possession of hypoglycemic and anti-aging effects [14]. Moreover, Kombucha in tea is reported to improve the shelf-life of the tea [15]. The tea harbors symbiosis of acetic acid bacteria (AAB), lactic acid bacteria (LAB), and yeasts [16]. The bacteria and yeast numbers can reach 106 colony forming units per milliliters (CFU/mL) in a culture which has been allowed to ferment for a period of 10 days. According to literature, the composition of yeast in the tea tends to outnumber the bacterial count [17]. These microorganisms assimilate different substrates in a tea as their carbon and nitrogen sources for their survival; consequently producing desired SCOBY products [18]. Thus, Kombucha tea is a potential reservoir for bioflocculant producing fungi.
The present study aimed at isolating and identifying a bioflocculant producing fungal strain from Kombucha tea SCOBY using conventional and 16S rRNA gene sequence analysis. The medium components and culture conditions of the isolate were optimized in order to improve yield and flocculating efficiency using the one-factor-at-a-time method. Finally, the extracted bioflocculant was characterized using scanning electron microscope (SEM) for evaluation of surface morphology, X-ray diffraction (XRD) for assessment of its crystallinity, and Fourier-transform infrared (FT-IR) for functional groups.

2. Materials and Methods

2.1. Isolation of Bioflocculant-Producing Fungi

The Kombucha tea with a SCOBY was purchased from Greenheart Organics Pinetown in Durban KwaZulu-Natal Province, delivered to the University of Zululand at Kwa-Dlangezwa, in the province of KwaZulu-Natal in South Africa and used for bioflocculant production. Kombucha tea was prepared as follows: the tea (1/2 cup of sugar and two ordinary tea bags) was boiled with sterilized distilled water in a clean beaker (1000 mL) (ChemLabs, Johannesburg, South Africa). Afterwards, the tea was cooled, the starter culture (SCOBY) was then added. Lastly, the jar (ChemLabs, Johannesburg, South Africa) was covered with a few layers of a tightly woven cloth and wrapped with a rubber band for 5 days at room temperature. The tea was then serially diluted using sterile saline water (0.85%) up to 10−5 dilution. For microbial isolation, potato dextrose agar (PDA) (Masiye Labs, Johannesburg, South Africa) was used. About 100 μL of the diluted Kombucha tea broth was aseptically spread on agar plates (Reflecta Laboratory Supplies, Johannesburg, South Africa). Thereafter, the inoculated plates were incubated for 3 days at 37 °C to obtain colonies. After the incubation period had elapsed, the colonies obtained were picked based on divergence in morphology, size, and color. The selected isolates were further sub-cultured on fresh agar plates to obtain pure cultures and re-incubated. Pure cultures were stored at −80 °C in 50% glycerol (ChemLabs, Johannesburg, South Africa).

2.2. Isolates Fermentation Activation

A medium containing 10 g tryptone, 5 g sodium chloride, and 3 g beef extract (Reflecta Laboratory Supplies, Johannesburg, South Africa) was prepared in a liter of autoclaved distilled water. About 5 mL of the activation medium was transferred into dissimilar test tubes (Laboratory Consumables and Chemical Supplies Cc, Durban, South Africa) and autoclaved at 121 °C for 15 min. After autoclaving, the isolates were inoculated into the media and incubated for 24 h at 37 °C with a rotary shaker (Laboratory Consumables and Chemical Supplies Cc, Durban, South Africa) at 160 rpm [19].

2.3. Screening for Bioflocculant Production

The method by Chen et al. [19] was followed for the bioflocculant production of the isolates. Production medium consisting of 20 g glucose, 0.5 g urea, 0.1 NaCl, 0.3 g NH4SO4, 0.3 g MgSO4, 5 g K2HPSO4, 2 g KH2PSO4, and 0.5 g yeast extract (ChemLabs, Johannesburg, South Africa) was prepared in a liter of Kombucha tea broth. Conical flasks (250 mL) (Laboratory Consumables and Chemical Supplies Cc, Durban, South Africa) were used to pour the production medium (50 mL) and then autoclaved. Thereafter, each flask was inoculated with pure isolates. All the inoculated flasks were incubated for 3 days at 30 °C with shaking speed of 160 rpm. After three days of incubation, 2 mL of the fermented medium was pipetted into sterile Eppendorf tubes (Labotec (Pty) Ltd., Cape Town, South Africa) and centrifuged (Labex Pty. Ltd., Johannesburg, South Africa) at 8000 rpm for 15 min. The supernatant was used to evaluate the ability of the isolates to produce a bioflocculant with excellent flocculating activity.

2.4. Determination of the Flocculating Activity

The method used by Luo et al. [20] was employed for the assessment of flocculating activity of the broth cultures. Briefly, kaolin solution (4 g/L) (Laboratory Consumables and Chemical Supplies Cc, Durban, South Africa) was prepared in using autoclaved distilled water. About 100 mL of kaolin solution was poured in a 250 mL conical flask (Laboratory Consumables and Chemical Supplies Cc, Durban, South Africa) and mixed with 2 mL of cell-free supernatant and 3 mL of 1% CaCl2 (w/v) solution. The mixture was agitated for 1 min, poured into a 100 mL measuring cylinder, and allowed to stand for 5 min at room temperature to sediment. A crude bioflocculant was replaced with a sterile production medium for a control. The optical density (OD) of the treated solution was measured at a wavelength of 550 nm using a spectrophotometer (Spectro-quant, Pharo 300 Merck, Boston, MA, USA). The following equation was utilized to calculate the percentage (%) flocculating activity.
Flocculating   activity   ( FA ) = [ A − B A ] × 100 %
where A is the OD at 550 nm of kaolin clay suspension and B is the optical density at 550 nm of the treated solution.

2.5. Identification and Purification of Fungi

The strain with the highest promising flocculating activity against kaolin clay suspension was selected, and identified using molecular technique. The genome DNA of the yeast was extracted by a ZR Fungal/Bacterial Kit™ (Zymo Research, Catalogue No. D6005, New York, NY, USA) according to the manufacturer’s instructions. Polymerase chain reaction (PCR) was employed to amplify of the fungal ribosomal RNA gene by the primers ITS1: 5′-TCCGTAGGTGAACCTGCGG-3′ and ITS4: 5′-TCCTCCGCTTATTGATATGC-3′, using OneTaq™ Quick Load 2x Master Mix (NEB, Catalogue No. M0486 Ipswich, MA, USA). PCR products were run on gel, followed by gel extraction using Zymoclean™ Gel DNA Recovery kit (Zymo Research, Catalogue No. D4001, Ipswich, MA, USA). The obtained fragments were sequenced in the forward and reverse directions on Nimagen, Brilliantdye™ Terminator Cycle Sequencing Kit V3.1, BRD3-100/1000 and cleaned by Zymo Research, ZR-96, DNA Sequencing Clean-up Kit™, Catalogue No. D4050. The cleaned portions were analyzed by ABI PRISM™ 3500xl Genetic Analyzer. The cleaned sequencing products were analyzed by CLC Bio Main Workbench v7.6, followed by a BLAST search using the US National Center for Biotechnology Information (NCBI) database to ascertain the closest fungal strain [21].

2.6. Optimization of Culture Conditions for Bioflocculant Production

Temperature, fermentation time, initial pH, shaking speed, cations, inoculum size, and carbon and nitrogen sources are the major factors which were optimized to enhance and increase the production yield and flocculation efficiency of the selected isolate [22]. The selected isolate had the initial flocculating activity of 75% against kaolin solution.

2.6.1. Effect of Inoculum Size on Bioflocculant Production

To determine the optimum inoculum size for bioflocculant production, the broth culture ranging from 1% (v/v) (0.5 mL) to 5% (v/v) (2.5 mL) was made and inoculated into 100 mL conical flasks with 50 mL sterile production medium. The inoculated flasks were incubated at 30 °C for 72 h at 160 rpm. The flocculating activity was measured by mixing 3 mL of 1% (w/v) calcium chloride and 2 mL cell-free supernatant and 100 mL kaolin suspension (4 g/L) added in 250 mL conical flask (ChemLabs, Johannesburg, South Africa). The mixture was shaken thoroughly for 1 min, transferred into graduated measuring cylinder (100 mL) and allowed to stand at room temperature for 5 min for sedimentation. The clear supernatant was utilized to determine flocculating activity at 550 nm as described in Section 3.4. The inoculum size with the highest flocculating activity was used in all subsequent experiments [23].

2.6.2. Effect of Carbon and Nitrogen Sources on Bioflocculant Production

Different carbon sources such as lactose, galactose, glucose, starch, sucrose xylose, and maltose were used, replacing glucose in the original production mediums. The isolate was inoculated in the production medium and incubated at 30 °C for 72 h in a shaker at 160 rpm. Flocculating activity determination was conducted after 3 days of incubation. The effect of different nitrogen sources (peptone, yeast extract, (NH4)2SO4, NH4Cl, and urea) on flocculating activity, were used. The equivalent amount (1.2 g/L) of the multiple nitrogen sources (urea, yeast extract, and (NH4)2SO4) (ChemLabs, Johannesburg, South Africa) used in the original medium was replaced with each nitrogen source, separately. The isolate was inoculated and incubated at 30 °C, 160 rpm for 72 h [20]. After incubation, the flocculating activity was measured as described previously. The carbon and nitrogen sources that showed the highest flocculating activity were used for further research.

2.6.3. The Effect of Agitation on the Production of a Bioflocculant

The method described by Zhang et al. [11] was followed to assess the dissimilar shaking speed effect on the flocculating activity. The assessed shaking speeds were 60, 80, 100, 120, 140, 160, and 180 rpm. Conical flasks (250 mL) with production media of 50 mL were inoculated with the optimum inoculum size (v/v) of the bioflocculant-producing isolate and incubated at 30 °C for 72h at dissimilar shaking speed ranges of 60–180 rpm. After 72 h of fermentation, the flocculating activity was determined for the different shaking speeds and the shaking speed that showed the highest flocculating activity was used for all the experiments followed.

2.6.4. Effect of Initial pH on Bioflocculant Production

The initial pH effect on bioflocculant production was evaluated by varying pH of the production medium with 0.1 M HCl and 0.1 M NaOH (ChemLabs, Johannesburg, South Africa) to adjust it to pH values ranging from 3 to 12. The pH adjustment was made before the production medium was sterilized. Thereafter, the isolate was inoculated and incubated at 30 °C, 160 rpm. After 72 h of cultivation, the flocculating activity was measured for each pH value as described previously and the pH value with the highest flocculating activity was used in all subsequent experiments [24].

2.6.5. Effect of Cations on Flocculating Activity

The cations impact on the flocculating activity was evaluated using the method by Nie et al. [25]. From the basal medium, the 1% (w/v) CaCl2 (ChemLabs, Johannesburg, South Africa) was replaced with different metal salt solutions (1% w/v) (LiCl, FeCl3, NaCl, BaCl2, MnCl2, KCl, and AlCl3) (ChemLabs, Johannesburg, South Africa). Each of the above cation was prepared and poured into a 250 mL conical flask with 100 mL kaolin solution and 2 mL of cell-free supernatant, shaken for 60 s, transferred to a 100 mL measuring cylinder (Laboratory Consumables and Chemical Supplies Cc, Durban, South Africa), and left to stand at room temperature for 5 min. To prepare the control experiment, the mixture of 100 mL kaolin solution and cell free supernatant was made without the addition of cations. The flocculating activity was measured as described previously and the cation with the highest effect on flocculating activity was used in all subsequent tests.

2.6.6. Effect of Cultivation Temperature on Bioflocculant Production

The method of Xia et al. [26] was used for determination of the effect of cultivation temperature on flocculating activity. The different temperatures (20, 25, 30, 35, 40, 45, 50, 55, and 60 °C) were used for incubation after the inoculation of the isolate in the production medium for a period of 72 h. After fermentation, the flocculating activity was measured and the temperature that showed the highest flocculating activity was used for further research.

2.6.7. Time Course

The method described by Okaiyeto et al. [27] was employed for the determination of fermentation time. The obtained optimum medium components and culture conditions were all used during the determination of the effect of time on flocculating activity, pH and microbial growth. Thus, the isolate was inoculated into the optimum autoclaved production medium and incubated under the obtained culture conditions. Sample (2 mL) was drawn at 12 h intervals for 120 h to evaluate the flocculating activity, pH, and microbial growth by measuring the OD at 660 nm.

2.7. Extraction and Purification of a Bioflocculant

The method by Chen et al. [28] was used during extraction and purification of the bioflocculant. After 60 h of fermentation, the fermented broth was centrifuged at 8000 rpm for 15 min to remove cells. About 1 volume (1000 mL) of distilled water was added into the cell-free supernatant, mixed properly, and re-centrifuged at 8000 rpm for 15 min. About 2 volumes (2000 mL) of ethanol was then added, agitated, and stored for 12 h at 4 °C. To obtain the crude bioflocculant, after 12 h the formed precipitate was vacuum dried. The crude bioflocculant was then re-dissolved in distilled water (100 mL) (w/v). Thereafter, the mixture of butanol and chloroform (5:2 v/v) (100 mL) was added. The mixture was thoroughly shaken and left at room temperature to stand for 12 h. The precipitate was then centrifuged at 8000 rpm for 15 min and vacuum-dried to obtain a purified bioflocculant. The weight of the dried purified bioflocculant was measured and expressed in g/L.

2.8. Bioflocculant Surface Morphology Analysis

Scanning electron microscopy (SEM) (SEM-Sipma-VP03-67, Zeiss, and P-Sigma, Munich, Germany), was used for the assessment of morphological structure of the purified bioflocculant. The bioflocculant was placed on the silicon-coated slide and fixed with a spin coater at 1000 rpm for 1 min. The surface appearance of the flocculated kaolin clay and kaolin clay particles were also investigated in the same way.

2.9. Chemical Analysis of the Purified Bioflocculant

2.9.1. Fourier Transform Infrared Spectrophotometer (FT-IT) Analysis

The FT-IR spectroscopy (Perkin Elmer System 2000, Cambridge, UK) was used to evaluate the functional groups of the purified bioflocculant. The purified bioflocculant (3 mg) was subjected to FT-IR spectroscopy. The sample was run at room temperature in the wavelength ranges of 4000–400 cm−1 after being mixed with potassium bromide (KBr).

2.9.2. X-ray Diffraction Analysis of the Bioflocculant

A Bruker D8 Advance diffractometer (Johannesburg, Burker 2190, South Africa) equipped with Cu-Kα radiation (1.5406) at 40 kV, 40 mA was utilized to investigate the crystallinity of the bioflocculant at room temperature. The bioflocculant were put on a sample holder, and the patterns of diffraction were recorded from 0 to 80 degrees [29].

2.10. Flocculation of a Purified Bioflocculant

2.10.1. Effect of Dosage Concentration on Flocculating Activity

The method described by Makapela [30] was utilized to determine the purified bioflocculant dosage concentration effect on flocculating activity. Concentration ranges of the bioflocculant solutions were prepared in a range between 0.2 and 1.0 mg/mL (w/v). The bioflocculant solution (2 mL) for each concentration was mixed with the kaolin clay suspension (100 mL) and 3 mL of 1% (w/v) NaCl in a conical flask (250 mL) and vigorously shaken. A standing graduated measuring cylinder (100 mL) was used to transfer the thoroughly shaken solution and was allowed to stand for 5 min at room temperature to sediment. As previously described, the flocculating activity of the clear supernatant was determined.

2.10.2. Effect of Heat on Flocculating Activity

The thermal stability of the bioflocculant was assessed within the range of 50–121 °C. To evaluate the thermal stability, 10 mL of the bioflocculant solution (0.4 mg/mL) was heated for 30 min at different temperatures. Afterwards, the heated bioflocculant solution (2 mL) was poured into a mixture of kaolin clay suspension (100 mL) and 3 mL of 1% (w/v) NaCl in a conical flask (250 mL). The mixture was agitated and allowed to stand for 5 min. Thereafter, the flocculating activity was measured as described previously [31].

2.10.3. Effect of pH on Flocculating Activity

The pH stability of the purified bioflocculant was determined. Before the determination of flocculating activity against pH, kaolin solution (4 g/L) (100 mL) was adjusted to pH range of 3–12 using 0.1 M NaOH or 0.1 M HCL (ChemLabs, Johannesburg, South Africa). Then, 2 mL of 0.4 mg/mL solution of a bioflocculant, 3 mL of 1% NaCl (w/v), and kaolin solution (100 mL) were mixed. The flocculating capability of the bioflocculant was then calculated [26].

2.10.4. Effect of NaCl Concentration on Flocculating Activity

The method used by Maliehe et al. [23] was adopted for the evaluation of the effect of salinity of the bioflocculant. By varying the different NaCl concentrations in a range of 5–30 g/L in kaolin solution (4 g/L), the effect of salinity on bioflocculant’s flocculating activity was studied.

2.11. Statistical Analysis

All data were collected in triplicates with mean and standard deviation values determined where differences were considered significant at 0.05 at confidence level (p > 0.05) by the use of Graph Pad Prism version 6. The significance was evaluated by variance analysis (ANOVA).

3. Results and Discussion

3.1. Isolation and Identification of Fungi with Bioflocculant-Producing Potential

The Kombucha tea SCOBY was used as the source for the isolation of the bioflocculant-producing microorganisms. Dilutions were made to obtain pure cultures and the obtained pure cultures were screened for bioflocculant production potential. Three isolated microorganisms were screened for bioflocculant production against kaolin clay suspension (4 g/L). The isolate with the highest flocculating activity (75%) was selected. The isolate was further identified using 16S rRNA sequencing method. In the GenBank database, the isolates comparative analysis of its 16S rRNA sequence showed 99% similarities with Pichia kudriavzevii and the accession number of the isolate was MH545928.1. Therefore, the isolate was named Pichia kudriavzevii MH545928.1. P. kudriavzevii, previously known as Issatchenkia orientalis, is the teleomorph of the Candida krusei. It is abundant in the environment and commonly found in soil, on the skins of fruits, as well as in fermented beverages. Like most yeast, P. kudriavzeii is predominately used in the fermentation of wine and beer [32]. However, to the best of our knowledge, this fungus has not been reported as a bioflocculant-producer.

3.2. Optimization of Culture Conditions for Bioflocculant Production

Bioflocculant production is reported to be influenced by factors such as carbon and nitrogen sources, oligoelements, and operating parameters (inoculum size, temperature, pH, aeration rate, etc.) [33]. In order to increase the bioflocculant production by P. kudriavzevii MH545928.1 and the 75% activity, different growth factors were optimized using the one-factor-at-a-time method.

3.2.1. Effect of Inoculum Size on Bioflocculant Production

The literature reveals that inoculum size is important for flocculating activity of a bioflocculant and during its production. Muthudineshkumar and Anand, Ref. [34] reported that the excessive inoculum size could clump-up the microorganisms and result in the inhibition of bioflocculant production while the insufficient inoculum size might lead to a delay of growth of microbes resulting to the poor bioflocculant production. It was observed that the bioflocculant was optimally produced when the inoculum size was 1% (v/v) with the flocculating activity of 95% (Figure 1). The increase in inoculum sizes from 1% (0.5 mL) led to a decrease in flocculating activity. The lowest activity of 67% was observed at the inoculum size of 5% (2.5 mL). A large inoculum probably made the niche of the P. kudriavzevii MH545928.1 to overlap excessively and inhibit the bioflocculant production. A bioflocculant produced by Aspergillus flavus was reported to attain the highest flocculating activity of 86.6% when 2% (v/v) inoculum size was used [35]. Therefore, each and every microorganism has its preferred inoculum size for optimal production of the bioflocculant. Thus, in all the experiments that followed, the inoculum size of 1% (v/v) was used in this study.

3.2.2. Effect of Carbon Source on the Production of a Bioflocculant

Carbon sources are considered as key factors during the bioflocculant production as they enhance the growth and production rate; thus, dissimilar microorganisms have varied preference for carbon sources [36]. The effect of various carbon sources on the production of a bioflocculant by P. kudriavzevii MH545928.1 was investigated and the results are depicted in Table 1. It was observed that among the studied carbon sources, glucose was the most preferred carbon source with 94.8% flocculating activity. All tested carbon sources were effective for production of the bioflocculant with more than 70% flocculating activity. The findings were in agreement with other studies, which stated that glucose is the most preferred carbon source for P. kudriavzevii MH545928.1 [37,38]. Glucose was then used for all subsequent experiment.

3.2.3. Effect of Nitrogen Source on Bioflocculant Production

With respect to the requirements for nitrogen sources, it has been found that different microorganisms prefer different nitrogen sources for their efficient growth and production of bioflocculant [39]. Peptone, yeast extract, urea, ammonium sulphate, ammonium nitrate, and casein were the nitrogen sources evaluated for their effect on bioflocculant production by P. kudriavzevii MH545928.1. Peptone was the most preferred nitrogen source with the flocculating activity of 94% (Table 1). Ammonium sulphate and urea were the least preferred nitrogen sources with the flocculating activity of 72%. Therefore, peptone was used in the production of bioflocculant by P. kudriavzevii MH545928.1. These results are in accordance with the results reported by Deng et al. [38], whereby Aspergillus parasiticus optimally produced a bioflocculant when peptone was utilized as a sole nitrogen source.

3.2.4. Effect of Agitation on the Bioflocculant Production

Lopez-Lopez et al. [40] reported that a continuous agitation of a production medium results in an aerobic growth stimulation as it enhances solubility of oxygen. From Figure 1, it can be observed that the low shaking speeds (60, 80, and 100 rpm) did not favor bioflocculant production by P. kudriavzevii MH545928.1. The bioflocculant production was favored by the optimum shaking speed of 140 rpm and yielded the flocculating activity of 96%. The optimum agitation provided sufficient oxygen requirement by P. kudriavzevii MH545928.1 during its growth phase and bioflocculant production [32]. The results were in close conformity with those reported by Piyo et al. [41], whereby the best flocculation was obtained at 160 rpm. The similarities was attributed to the same oxygen demand by the microorganisms at different growth stages [39].

3.2.5. Effect of Cultivation Temperature on Bioflocculant Production

Maximum enzymatic activities take place at optimum temperatures for microbial growth and bioflocculant production. Thus, the growth temperature significantly affects fungal growth, bioflocculant production, and consequently flocculating activity [42]. The effect of temperature was investigated on bioflocculant production by P. kudriavzevii MH545928.1 and the most effective temperatures were 30–45 °C as shown on the Table 1. The highest flocculating activity of 97% was observed at temperature of 35 °C while the lowest temperature (20 °C) resulted in the least flocculating activity (69%). A rise in temperature above optimum tends to increase fungal growth, metabolic functions, and bioflocculant production until the point where denaturation of biomolecules, such as proteins, set in [43]. On the other hand, low temperatures may slow down the rate of metabolic processes, such as cell wall polymer synthesis, consequently leading to poor growth and metabolite production [44]. The two phenomena were observed in this study. The highest flocculating activities of bioflocculants were reported when the microorganisms were cultured at 30 °C [45].

3.2.6. Effect of Cations on Bioflocculant Production

Cations have been found to either inhibit or stimulate the production of bioflocculants [46,47]. Mechanisms involved in stimulation are stabilization and neutralization of the residual charge of functional groups on the bioflocculant by the cations [38]. The suspension solution of metal ions results in the increase of the ionic strength because of the addition of the metal ion; thus, reducing electrostatic forces of the suspended impurities [16]. The various cations’ effect on flocculating activity of the production of the bioflocculant by P. kudriavzevii MH545928.1 was studied and the results are shown Table 1. The different cations ions including monovalent (Na+, K+, and Li+), divalent (Mn2+ and Ba2+), and trivalent (Al3+ and Fe3+) and the control were evaluated. The monovalent NaCl showed the highest flocculating activity of 95%, followed by divalent MnCl2 and BaCl2 with flocculating activity of 78 and 84%, respectively. Other metal ions such as AlCl3, FeCl3, KCl, and LiCl also gave flocculating activities above 70%. Thus, the bioflocculant seems to be cation dependent with the control (no cation) showing less than 40% flocculating activity. Nevertheless, Lian, [48] reported that some microorganisms do not require addition of cations for their optimum bioflocculant production. Contrary to the study findings, a bioflocculant produced by Bacillus sp. AEMREG4 was reported to show low flocculating activity of 67.7% for Na+ (monovalent cation) and Al3+ (trivalent cation) showed the highest flocculating activity (83.3%) [49]. Therefore, Na+ cation was used in all subsequent experiments in this study.

3.2.7. Effect of Initial pH on Bioflocculant Production

Dissimilar microbes prefer varied pH ranges for the production of bioflocculants. The initial pH of the culture medium influences the electric charge of the microbial cells and the redox potential that can have an impact on enzymatic reactions and nutrient absorption [41]. Table 1 depicts the effect of the initial pH of the medium on bioflocculant production. Over the pH range of 3–7, the lowest flocculating activity was 53%; within the range of pH 7–12, the least activity (68%) was obtained when the initial pH was 12. The optimal pH for bioflocculant production for P. kudriavzevii pH 7 and pH 9, which gave the flocculating activity of 91%. Therefore, pH 7 was used for all subsequent tests as it could save the amount of alkaline and acid solutions required to adjust the pH, consequently reducing the cost of production. These findings are in accordance with the study by [32], whereby Aspergillus flavus MCB 271 and Aspergillus niger MCBF 08 produced a bioflocculant optimally at pH 7.

3.2.8. Time Course on Production for Bioflocculant

The growth curve for the microorganism according to flocculating activity, optical density (OD660nm), and pH is depicted in Figure 2. The optimal flocculation conditions that were obtained previously from the experiments were utilized for the growth curve. The yeast P. kudriavzevii MH545928.1 was examined for the production of a bioflocculant during the growth curve (120 h). The microbe was able to optimally produce the bioflocculant at 60 h of cultivation with flocculating activity of 99.1%. After 60 h of fermentation, the flocculating activity declined constantly. It has been observed that nutrients deficiency is in direct proportion to the decline of the cell growth from the production medium of the microorganism. This explains the reason for a reduction in flocculating activity of the bioflocculant production after 60 h. In general, the reduction may also be in correlation to the bioflocculant degrading enzyme that is produced and released; in turn, the produced bioflocculant is utilized as a source of carbon, or this depletion may be the result of autolysis. The findings were in accordance to those of Deng et al. [38], who reported that Aspergillus parasiticus produced bioflocculant with maximum flocculating activity (98.1%) after 60 h. This confirms that some fungi are able to produce bioflocculant with maximum flocculating activity during the early stationary phase of their cultivation. Contrary to these study findings, other studies have shown that some bioflocculants are produced at the late stationary phase of cultivation [50]. It was suggested that the decrease in the flocculation activity observed after 60 h could be attributed to the molecular weight decrease in the bioflocculant due to protease hydrolysis due to the decrease in pH [51]. A direct proportionality was also observed in the study between optical density and flocculation activity. The similarities shown by the growth and activity is an indication that the bioflocculant was not produced by autolysis of cells, rather by a biosynthesis process [52]. The pH of the production medium decreased from pH 7.05 to pH 6 during the exponential production of the bioflocculant. Thereafter, it increased from pH 6 up to pH 7.0 at which it remained constant for 48 h during bioflocculant production and decreased to pH 5.5. The decrease might be attributed to organic acids secreted by P. kudriavzevii MH545928.1 during metabolic reactions [52]. A bioflocculant IH-7 produced by A. flavus presented similar findings to the current study where pH was seen to decrease from pH 7.0 to 5.3 within 48 h of fermentation, then it increased insignificantly after 96 h to pH 5.6 [3].

3.3. Extraction and Purification of the Bioflocculant

The crude bioflocculant produced by P. kudriavzevii MH545928.1 strain after extraction was 3.6 g/L. The colour substance of the bioflocculant was a milky white. The extract was then partially purified using a mixture of chloroform and butanol (5:2 v/v), which yielded a white powdered substance weighing about 2.836 g/L. This yield is better when compared to the one reported by Fang and Shi [53], whereby Talaromyces trachyspermus OU5 produced 1.21 g/L of the bioflocculant. Zhang et al. [11] reported a yield of 14.8 g/L bioflocculant from the organism Myxobacterium nannocystics sp. NU-2, which is 4 times to the yield obtained in this study. Li et al. [54] also reported that Paenibacillus elgii B69 produced a bioflocculant of 25.63 g/L utilizing sucrose as carbon source. Low yields and high costs present significant practical application constraints in the production of bioflocculants [55]. Thus, it is suggested that in future P. kudriavzevii MH545928.1 in fungal consortia is used in order to further improve bioflocculant yield and flocculating activity.

3.4. Characterization of the Purified Bioflocculant

3.4.1. Functional Groups of the Bioflocculant

FT-IR analysis was undertaken to determine the presence of functional groups of the bioflocculant. The FT-IR spectrum revealed the presence of sharp band O-H stretching bond at 3723 cm−1, which indicated the availability of alcohol. The hydroxyl presence in the polymer favors hydrogen bonding possibilities with one or more molecules of water, which therefore, means in an aqueous solution, the bioflocculant is highly soluble [56]. A band stretching at 3304 cm−1 indicated the presence of secondary amine. The peaks at 2996 and 2925 cm−1 were attributed to the functional group C-H of stretching vibration of sugar residues constituents. The presence of a strong vibration peak was observed at 2354 cm−1, which indicated the presence of C-O. The peaks at 2193 and 2131 cm−1 were observed, indicative of the presence of weak alkyne and strong thiocynate, respectively. Alkynes are unsaturated hydrocarbons and have been found to have a higher boiling point which could be the reason for the observed flocculating activity of the bioflocculant at higher temperatures (Figure 3) [57].
The thiocynate functional group shows high solubility in water (177 g/100 mL (0 °C)) and has a high boiling point (500 °C), which could be the attributor effect to the bioflocculant being able to dissolve in water and show good flocculating activity even when autoclaved (121 °C) [58]. Sharp absorption vibrations were observed at 1660 and 1582 cm−1 indicating the presence of carbonyl functional groups, which have been said to allow the spreading out of the chain due to electrostatic repulsion [59]. A strong peak at 1416 cm−1 indicated the presence of sulfonyl functional group, which has asymmetrical stretching vibrations of S = O [3]. The presence of sugar was indicated by a small absorption peak at 1244 and 1169 cm−1, which showed C-O bonds. The aliphatic amine was revealed by the presence of strong peaks showed by the spectrum at 1060 cm−1 and 1045 cm−1. The presence of furan sugar (saccharide) was indicated by a sharp peak at 894 cm−1 and a strong peak stretching at 607 and 520 cm−1 represented a halo compound. The strong absorption peak present at 1100 and 1200 cm−1 and the functional groups (carboxyl and hydroxyl) that are available in the molecular chain of a bioflocculant are known to be general characteristics of all sugar derivatives [52]. From these observations it can be deduced that the bioflocculant consist of a polysaccharide as its main constituent. The detected functional groups were thought to be responsible in the bioflocculant’s flocculation process [60]. The observed findings were also in line with the findings of other researchers for the FT-IR spectrum produced by variety of bioflocculants [61].

3.4.2. Crystallinity of the Bioflocculant

The X-ray pattern illustration of the bioflocculant at angle (2θ) is depicted in Figure 4 with deep peaks observed between 10° and 40° angles. The strong peaks shown on the bioflocculant are very intense which could mean that the bioflocculant may have some impurities [62] The broadening of peaks in solid XRD pattern is usually due to particle size effect. Broader peaks signify smaller particle size, and this means the bioflocculant produced in this study has bigger particles as the bioflocculant does not show any broad peaks.

3.4.3. Surface Morphology of the Bioflocculant

In the flocculation process, the surface morphological structure of the bioflocculant is of great importance [63]. It determines the effectiveness of bioflocculants during flocculation process. Figure 5 shows images obtained using a scanning electron microscope. The image of a cumulus-like form of bioflocculant was shown (Figure 5a). The bioflocculant high-flocculating activity could be due to its configuration. The structure of the kaolin particles seemed to be fine and smooth (Figure 5b). The floc appeared clumped together after flocculation with bioflocculant (Figure 5c). The floc appeared to be interconnected as a result of the flocculation process, which allowed particles to be absorbed onto the bioflocculant, resulting in larger flocs.

3.5. Flocculation Properties of the Purified Bioflocculant

3.5.1. Dosage Size Effect on Flocculating Activity

In deciding bioflocculant efficiency, dosage concentration is a critical factor. Inadequate or excessive dosage can lead to inhibition in bioflocculant performance. Moreover, appropriate dosage sizes minimize expenses [64]. Thus, the effect of the dosage size was evaluated. The flocculating activity of the bioflocculant initially increased with the increase in dosage size; a subsequent decrease in activity was observed at dosage sizes higher than 0.4 mg/mL. The maximum flocculating activity of 80% was obtained at 0.4 mg/mL and the lowest activity (28.3%) was at 1 mg/mL (Table 2). Similar results were reported, whereby 0.4 mg/mL dosage size was found to have high flocculating activity (Table 3) [65]. The dosage concentration of 0.4 mg/mL was used for all the experiments that followed.

3.5.2. Effect of Temperature on the Bioflocculant

The thermal stability of the bioflocculant (0.4 mg/mL) was evaluated by varying different temperatures and the results are depicted in Table 2. The increase in temperature led to a slight decreased in the flocculating activity. The highest flocculating activity of 79% was observed at 50 °C and the lowest activity (65%) was seen at 121 °C. Pu; [66] observed similar findings where bioflocculant from Aspergillus niger (A18) retained the flocculating activity above 83% at 100 °C (Table 3). Thus, the bioflocculant is considered a thermally stable molecule. This could imply that the bioflocculant is predominately polysaccharide, which is confirmed by the identified functional groups (Figure 2) [32]. Protein rich bioflocculants have poor thermal resistance than those of polysaccharides. Thus, the slight loss of activity at high temperatures might be attributed to the denaturation of proteinous components [48]. Bioflocculants with high sugar content are reported to be heat stable and can retain more than fifty percent of their flocculating activity when exposed to high temperatures [49].
The bioflocculant produced from P. kudriavzevii was well comparable with other fungal bioflocculants from other researchers.

3.5.3. Effect of pH on Flocculating Activity on the Bioflocculant

The flocculation process is mainly influenced by pH, which can be considered as the key factor in reaction mixture. Literature states that the alteration of pH may affect the bioflocculant electric status and physiognomies of suspended particles, consequently altering the flocculating activity [45]. In this study, the effect of pH on flocculating activity of the purified bioflocculant was assessed and the results are shown in Table 3. The bioflocculant had a promising flocculating activity at neutral, and at slightly alkaline pH conditions (pH 8–9). The peak flocculating activity was observed at pH 8 (69.1%) and the lowest (35%) at pH 5. The changes in the activity might be due to the changes in pH due to the fact that the bioflocculant and kaolin particles exhibited various electric states at different pH values [28]. At acidic conditions, the bio-flocculant and kaolin particles might have absorbed hydrogen ions (H+), which weakened the formation of the bioflocculant-kaolin complexes, resulting in poor flocculating activity. However, at the optimum pH of 8, the hydroxide ion (OH−) absorbed promoted the formation of the complexes (bioflocculant-kaolin particles), consequently leading to effective flocculating action. The promising flocculating activity of the bioflocculant at neutral and slight basic conditions indicates its ability to be used in different biotechnological applications. Contrary to these findings, Nie et al. [24], reported that a bioflocculant obtained from Aspergillus oryzae had optima flocculating activity at pH 5 (93%) (Table 3).

3.5.4. Effect of Salinity on Flocculating Activity of the Bioflocculant

High salinity tends to interfere with bioflocculants’ activity. The effect of salt concentration on the flocculating activity of the bioflocculant (0.4 mg/mL) was assessed and the results are displayed in Table 3. There was a constant decrease in flocculating activity with the increase in salt concentration. The highest activity of 81% was obtained at the lowest NaCl concentration of 5 g/L while the least activity (40%) was observed at 30 g/L. The decrease in activity could be attributed to the excessive of Na+ interfering with the agglomeration between kaolin particles and the functional groups of the bioflocculants. Moreover, the bioflocculants’ physical properties might have been changed due to the high Na+ concentrations [68]. Contrary to these findings, Satyanarayana et al. [69], reported the highest flocculating activity of 94.3% by the bioflocculant at the high salinity (25 g/L). From these findings, it can be deduced that the bioflocculant produced by P. kudriavzevii MH545928.1 can only be effectively used in environments with low NaCl concentrations.

4. Conclusions

The study showed that the fungal strain P. kudriavzevii MH545928.1 produce bioflocculant with high flocculating activity under optimum medium components and culture conditions. It also produces moderate bioflocculant yield when compared with other fungal strains. Its morphological structure, diverse functional groups (hydroxyl, carboxyl, amine, and thiocynates) and crystallinity are responsible for its profound flocculating activity. Moreover, the bioflocculant is effective at low dosages size (0.4 mg/mL), saline sensitive, and is thermally stable when exposed to different temperatures. The revealed properties suggested its potential applicability in industrial fields. For further studies, the bioflocculant will be applied in treatment of wastewater and dye removal.

Author Contributions

Conceptualization, A.K.B., R.V.S.R.P., and Z.G.N.; formal analysis, T.S.M.; investigation, P.H.T.; supervision, A.K.B., R.V.S.R.P., and Z.G.N.; Writing—original draft, P.H.T.; Writing—review and editing, T.S.M. All authors have read and agreed to the published version of the manuscript.

Funding

The research was sponsored by CSIR (Council for Scientific and Industrial Research) South Africa (Grant No: F171).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

The authors would like to acknowledge the staff and postgraduate students (Biofloc Group) in the Department of Biochemistry and Microbiology for their outstanding support.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Ma, F.; Duan, S.; Kong, X.; Chen, X.; Yang, J.; Wang, A. Present status and development trend of studies on microbial flocculants. China Water Wastewater 2012, 28, 14–17. [Google Scholar]
  2. Abraham, J.; Singh, N.; Janapal, Y.; Kumar, N.U. Optimized bioflocculant production from Fungi using response surface methodology. Int. J. Pharm. Tech. Res. 2015, 8, 230–235. [Google Scholar]
  3. Aljuboori, A.H.R.; Idris, A.; Abdullah, N.; Mohamad, R. Production and characterization of a bioflocculant produced by Aspergillus flavus. Bioresour. Technol. 2013, 127, 489–493. [Google Scholar] [CrossRef] [PubMed]
  4. Gao, J.; Bao, H.-Y.; Xin, M.-X.; Liu, Y.-X.; Li, Q.; Zhang, Y.-F. Characterization of a bioflocculant from a newly isolated Vagococcus sp. W31. J. Zhejiang Univ. Sci. B 2006, 7, 186–192. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  5. Sam, S.; Kucukasik, F.; Yenigun, O.; Nicolaus, B.; Oner, E.T.; Yukselen, M.A. Flocculating performances of exopolysaccharides produced by a halophilic bacterial strain cultivated on agro-industrial waste. Bioresour. Technol. 2011, 102, 1788–1794. [Google Scholar] [CrossRef]
  6. Pu, L.; Zeng, Y.-J.; Xu, P.; Li, F.-Z.; Zong, M.-H.; Yang, J.-G.; Lou, W.-Y. Using a novel polysaccharide BM2 produced by Bacillus megaterium strain PL8 as an efficient bioflocculant for wastewater treatment. Int. J. Biol. Macromol. 2020, 162, 374–384. [Google Scholar] [CrossRef]
  7. Patil, S.V.; Patil, C.D.; Salunke, B.K.; Salunkhe, R.B.; Bathe, G.; Patil, D.M. Studies on characterization of bioflocculant exopolysaccharide of Azotobacter indicus and its potential for wastewater treatment. Appl. Biochem. Biotechnol. 2011, 163, 463–472. [Google Scholar] [CrossRef] [PubMed]
  8. Pathak, M.; Sarma, H.K.; Bhattacharyya, K.G.; Subudhi, S.; Bisht, V.; Lal, B.; Devi, A. Characterization of a novel polymeric bioflocculant produced from bacterial utilization of n-hexadecane and its application in removal of heavy metals. Front. Microbiol. 2017, 8, 170. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  9. Wauer, G.; Teien, H.-C. Risk of acute toxicity for fish during aluminium application to hardwater lakes. Sci. Total Environ. 2010, 408, 4020–4025. [Google Scholar] [CrossRef]
  10. Peleg, M.; Corradini, M.G. Microbial growth curves: What the models tell us and what they cannot. Crit. Rev. Food Sci. Nutr. 2011, 51, 917–945. [Google Scholar] [CrossRef]
  11. Zhang, Z.-Q.; Bo, L.; Xia, S.-Q.; Wang, X.-J.; Yang, A.-M. Production and application of a novel bioflocculant by multiple-microorganism consortia using brewery wastewater as carbon source. J. Environ. Sci. 2007, 19, 667–673. [Google Scholar] [CrossRef]
  12. Ben Rebah, F.; Mnif, W.; M Siddeeg, S. Microbial flocculants as an alternative to synthetic polymers for wastewater treatment: A review. Symmetry 2018, 10, 556. [Google Scholar] [CrossRef] [Green Version]
  13. Tlou, N.S. Characterization of Selected Microbial Species for Bioflocculant Producing Potential and Comparison with Traditional Flocculants in Industrial Waste Water Treatment; University of Zululand: Richards Bay, South Africa, 2017. [Google Scholar]
  14. Sánchez-Porro, C.; Martin, S.; Mellado, E.; Ventosa, A. Diversity of moderately halophilic bacteria producing extracellular hydrolytic enzymes. J. Appl. Microbiol. 2003, 94, 295–300. [Google Scholar] [CrossRef] [PubMed]
  15. La Torre, C.; Fazio, A.; Caputo, P.; Plastina, P.; Caroleo, M.C.; Cannataro, R.; Cione, E. Effects of Long-Term Storage on Radical Scavenging Properties and Phenolic Content of Kombucha from Black Tea. Molecules 2021, 26, 5474. [Google Scholar] [CrossRef] [PubMed]
  16. Watawana, M.I.; Jayawardena, N.; Gunawardhana, C.B.; Waisundara, V.Y. Health, wellness, and safety aspects of the consumption of kombucha. J. Chem. 2015, 2015, 591869. [Google Scholar] [CrossRef] [Green Version]
  17. Sinir, G.Ö.; Tamer, C.E.; Suna, S. Kombucha tea: A promising fermented functional beverage. In Fermented Beverages; Elsevier: Amsterdam, The Netherlands, 2019; pp. 401–432. [Google Scholar]
  18. Goh, C.H.; Heng, P.W.S.; Chan, L.W. Alginates as a useful natural polymer for microencapsulation and therapeutic applications. Carbohydr. Polym. 2012, 88, 1–12. [Google Scholar] [CrossRef]
  19. Četojević-Simin, D.D.; Velićanski, A.S.; Cvetković, D.D.; Markov, S.L.; Mrđanović, J.Ž.; Bogdanović, V.V.; Šolajić, S.V. Bioactivity of lemon balm kombucha. Food Bioprocess Technol. 2012, 5, 1756–1765. [Google Scholar] [CrossRef]
  20. Luo, Z.; Chen, L.; Chen, C.; Zhang, W.; Liu, M.; Han, Y.; Zhou, J. Production and characteristics of a bioflocculant by Klebsiella pneumoniae YZ-6 isolated from human saliva. Appl. Biochem. Biotechnol. 2014, 172, 1282–1292. [Google Scholar] [CrossRef]
  21. Pryce, T.; Palladino, S.; Kay, I.; Coombs, G. Rapid identification of fungi by sequencing the ITS1 and ITS2 regions using an automated capillary electrophoresis system. Med. Mycol. 2003, 41, 369–381. [Google Scholar] [CrossRef]
  22. Ray, A.; Banerjee, S.; Das, D. Microalgal bio-flocculation: Present scenario and prospects for commercialization. Environ. Sci. Pollut. Res. 2021, 28, 1–19. [Google Scholar] [CrossRef]
  23. Maliehe, T.; Simonis, J.; Basson, A.; Reve, M.; Ngema, S.; Xaba, P. Production, characterisation and flocculation mechanism of bioflocculant TMT-1 from marine Bacillus pumilus JX860616. Afr. J. Biotechnol. 2016, 15, 2352–2367. [Google Scholar]
  24. Salehizadeh, H.; Yan, N.; Farnood, R. Recent advances in polysaccharide bio-based flocculants. Biotechnol. Adv. 2018, 36, 92–119. [Google Scholar] [CrossRef] [PubMed]
  25. Nie, M.; Yin, X.; Jia, J.; Wang, Y.; Liu, S.; Shen, Q.; Li, P.; Wang, Z. Production of a novel bioflocculant MNXY1 by Klebsiella pneumoniae strain NY1 and application in precipitation of cyanobacteria and municipal wastewater treatment. J. Appl. Microbiol. 2011, 111, 547–558. [Google Scholar] [CrossRef] [PubMed]
  26. Xia, S.; Zhang, Z.; Wang, X.; Yang, A.; Chen, L.; Zhao, J.; Leonard, D.; Jaffrezic-Renault, N. Production and characterization of a bioflocculant by Proteus mirabilis TJ-1. Bioresour. Technol. 2008, 99, 6520–6527. [Google Scholar] [CrossRef] [PubMed]
  27. Okaiyeto, K.; Nwodo, U.U.; Mabinya, L.V.; Okoh, A.I. Characterization of a bioflocculant produced by a consortium of Halomonas sp. Okoh and Micrococcus sp. Leo. Int. J. Environ. Res. Public Health 2013, 10, 5097–5110. [Google Scholar] [CrossRef] [Green Version]
  28. Chen, H.; Zhong, C.; Berkhouse, H.; Zhang, Y.; Lv, Y.; Lu, W.; Yang, Y.; Zhou, J. Removal of cadmium by bioflocculant produced by Stenotrophomonas maltophilia using phenol-containing wastewater. Chemosphere 2016, 155, 163–169. [Google Scholar] [CrossRef]
  29. Ntsaluba, L. Studies on Bioflocculant Production by a Consortium of Two Bacterial Species Belonging to the Methylobacterium and Actinobacterium Genera. Master’s Thesis, University of Fort Hare, Faculty of Science & Agriculture, Alice, South Africa, 2012. [Google Scholar]
  30. Makapela, B. Evaluation of Bioflocculant-Producing Potential of Bacillus Pumilus Strain Isolated from Tyume River in the Eastern Cape Province of South Africa. Master’s Thesis, University of Fort Hare, Alice, South Africa, 2015. [Google Scholar]
  31. Manheim, D.; Nelson, Y. Settling and bioflocculation of two species of algae used in wastewater treatment and algae biomass production. Environ. Prog. Sustain. Energy 2013, 32, 946–954. [Google Scholar] [CrossRef]
  32. David, O.; Oluwole, O.; Ayodele, O.; Lasisi, T. Characterisation of fungal bioflocculants and its application in water treatment. Curr. J. Appl. Sci. Technol. 2019, 34, 1–9. [Google Scholar] [CrossRef]
  33. Patiala, I. Studies on Polymeric Bioflocculant Producing Microorganisms. Master’s Thesis, Thapar Institute of Engineering and Technology, Patiala, India, 2005. [Google Scholar]
  34. Muthudineshkumar, R.; Anand, R. Anaerobic digestion of various feedstocks for second-generation biofuel production. In Advances in Eco-Fuels for a Sustainable Environment; Elsevier: Amsterdam, The Netherlands, 2019; pp. 157–185. [Google Scholar]
  35. Alonso-del-Real, J.; Pérez-Torrado, R.; Querol, A.; Barrio, E. Dominance of wine Saccharomyces cerevisiae strains over S. kudriavzevii in industrial fermentation competitions is related to an acceleration of nutrient uptake and utilization. Environ. Microbiol. 2019, 21, 1627–1644. [Google Scholar] [CrossRef] [Green Version]
  36. Dlamini, N.G. Biosynthesis of Copper Nanoparticles Using a Bioflocculant from Alcaligenis Faecalis, Characterization and Its Application. Master’s Thesis, University of Zululand, Richards Bay, South Africa, 2017. [Google Scholar]
  37. Dhaliwal, S.S.; Oberoi, H.S.; Sandhu, S.K.; Nanda, D.; Kumar, D.; Uppal, S.K. Enhanced ethanol production from sugarcane juice by galactose adaptation of a newly isolated thermotolerant strain of Pichia kudriavzevii. Bioresour. Technol. 2011, 102, 5968–5975. [Google Scholar] [CrossRef] [PubMed]
  38. Deng, S.; Yu, G.; Ting, Y.P. Production of a bioflocculant by Aspergillus parasiticus and its application in dye removal. Colloids Surf. B Biointerfaces 2005, 44, 179–186. [Google Scholar] [CrossRef] [PubMed]
  39. Mao, Z.; Xie, J.; Wang, A.; Wang, W.; Ma, D.; Liu, P. Effects of annealing temperature on the interfacial microstructure and bonding strength of Cu/Al clad sheets produced by twin-roll casting and rolling. J. Mater. Process. Technol. 2020, 285, 116804. [Google Scholar] [CrossRef]
  40. López-López, C.; Martín-Pascual, J.; Leyva-Díaz, J.C.; Martínez-Toledo, M.V.; Muñío, M.M.; Poyatos, J.M. Combined treatment of textile wastewater by coagulation–flocculation and advanced oxidation processes. Desalination Water Treat. 2016, 57, 13987–13994. [Google Scholar] [CrossRef]
  41. Nontembiso, P.; Sekelwa, C.; Leonard, M.V.; Anthony, O.I. Assessment of bioflocculant production by Bacillus sp. Gilbert, a marine bacterium isolated from the bottom sediment of Algoa Bay. Mar. Drugs 2011, 9, 1232–1242. [Google Scholar] [CrossRef]
  42. Rosu, C.M.; Avadanei, M.; Gherghel, D.; Mihasan, M.; Mihai, C.; Trifan, A.; Miron, A.; Vochita, G. Biodegradation and detoxification efficiency of azo-dye reactive orange 16 by Pichia kudriavzevii CR-Y103. Water Air Soil Pollut. 2018, 229, 1–18. [Google Scholar] [CrossRef]
  43. Mohammed, J.N.; Dagang, W.R.Z.W. Role of cationization in bioflocculant efficiency: A review. Environ. Process. 2019, 6, 355–376. [Google Scholar] [CrossRef]
  44. More, T.; Yadav, J.S.S.; Yan, S.; Tyagi, R.D.; Surampalli, R.Y. Extracellular polymeric substances of bacteria and their potential environmental applications. J. Environ. Manag. 2014, 144, 1–25. [Google Scholar] [CrossRef]
  45. Nakata, K.; Kurane, R. Production of an extracellular polysaccharide bioflocculant by Klebsiella pneumoniae. Biosci. Biotechnol. Biochem. 1999, 63, 2064–2068. [Google Scholar] [CrossRef] [Green Version]
  46. Nguyen, N.T.; Phan, T.H.M.; Tran, T.N.; Velmurugan, B.K.; Kiefer, R. Production of novel bio-flocculants from Klebsiella variicola BF1 using cassava starch wastewater and its application. Curr. Sci. 2019, 117, 00113891. [Google Scholar] [CrossRef]
  47. Ogunsade, O.O.; Bakare, M.K.; Adewale, I.O. Purification and characterization of bioflocculant produced by Bacillus amyloliquefaciens ABL 19 isolated from Adeti Stream, Ilesa, Osun State, Nigeria. Nat. Sci. 2015, 13, 54–64. [Google Scholar]
  48. Lian, B.; Chen, Y.; Zhao, J.; Teng, H.H.; Zhu, L.; Yuan, S. Microbial flocculation by Bacillus mucilaginosus: Applications and mechanisms. Bioresour. Technol. 2008, 99, 4825–4831. [Google Scholar] [CrossRef]
  49. Ntsangani, N.; Okaiyeto, K.; Uchechukwu, N.U.; Olaniran, A.O.; Mabinya, L.V.; Okoh, A.I. Bioflocculation potentials of a uronic acid-containing glycoprotein produced by Bacillus sp. AEMREG4 isolated from Tyhume River, South Africa. 3 Biotech 2017, 7, 78. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  50. Ngulube, T.; Gumbo, J.R.; Masindi, V.; Maity, A. An update on synthetic dyes adsorption onto clay based minerals: A state-of-art review. J. Environ. Manag. 2017, 191, 35–57. [Google Scholar] [CrossRef] [PubMed]
  51. Li, Z.; Zhong, S.; Lei, H.-y.; Chen, R.-w.; Yu, Q.; Li, H.-L. Production of a novel bioflocculant by Bacillus licheniformis X14 and its application to low temperature drinking water treatment. Bioresour. Technol. 2009, 100, 3650–3656. [Google Scholar] [CrossRef]
  52. Campos, V.; Fernandes, A.R.; Medeiros, T.A.; Andrade, E.L. Physicochemical characterization and evaluation of PGA bioflocculant in coagulation-flocculation and sedimentation processes. J. Environ. Chem. Eng. 2016, 4, 3753–3760. [Google Scholar] [CrossRef] [Green Version]
  53. Fang, D.; Shi, C. Characterization and flocculability of a novel proteoglycan produced by Talaromyces trachyspermus OU5. J. Biosci. Bioeng. 2016, 121, 52–56. [Google Scholar] [CrossRef]
  54. Li, N.-J.; Lan, Q.; Wu, J.-H.; Liu, J.; Zhang, X.-H.; Zhang, F.; Yu, H.-Q. Soluble microbial products from the white-rot fungus Phanerochaete chrysosporium as the bioflocculant for municipal wastewater treatment. Sci. Total Environ. 2021, 780, 146662. [Google Scholar] [CrossRef]
  55. Ndejiko, J.M.; Dagang, W.R.Z.W. Flocculation Behaviour of Bioflocculant Produced from Chicken Viscera; E3S Web of Conferences; EDP Sciences: Les Ulis, France, 2019; p. 01013. [Google Scholar]
  56. Pan, Y.; Shi, B.; Zhang, Y. Research on flocculation property of bioflocculant PG. a21 Ca. Mod. Appl. Sci. 2009, 3, 106–112. [Google Scholar] [CrossRef]
  57. Sarkar, B.; Chakrabarti, P.; Vijaykumar, A.; Kale, V. Wastewater treatment in dairy industries—possibility of reuse. Desalination 2006, 195, 141–152. [Google Scholar] [CrossRef]
  58. Wang, L.; Ma, F.; Qu, Y.; Sun, D.; Li, A.; Guo, J.; Yu, B. Characterization of a compound bioflocculant produced by mixed culture of Rhizobium radiobacter F2 and Bacillus sphaeicus F6. World J. Microbiol. Biotechnol. 2011, 27, 2559–2565. [Google Scholar] [CrossRef]
  59. Xiong, Y.; Wang, Y.; Yu, Y.; Li, Q.; Wang, H.; Chen, R.; He, N. Production and characterization of a novel bioflocculant from Bacillus licheniformis. Appl. Environ. Microbiol. 2010, 76, 2778–2782. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  60. Waites, M.J.; Morgan, N.L.; Rockey, J.S.; Higton, G. Industrial Microbiology: An Introduction; John Wiley & Sons: Hoboken, NJ, USA, 2009. [Google Scholar]
  61. Li, C.; Zhang, X.; Guo, Y.; Seidi, F.; Shi, X.; Xiao, H. Naturally Occurring Exopolysaccharide Nanoparticles: Formation Process and Their Application in Glutathione Detection. ACS Appl. Mater. Interfaces 2021, 13, 19756–19767. [Google Scholar] [CrossRef] [PubMed]
  62. Dlamini, N.G.; Basson, A.K.; Pullabhotla, V. Biosynthesis and characterization of copper nanoparticles using a bioflocculant extracted from alcaligenis faecalis HCB2. Adv. Sci. Eng. Med. 2019, 11, 1064–1070. [Google Scholar] [CrossRef]
  63. Kavita, K.; Singh, V.K.; Mishra, A.; Jha, B. Characterisation and anti-biofilm activity of extracellular polymeric substances from Oceanobacillus iheyensis. Carbohydr. Polym. 2014, 101, 29–35. [Google Scholar] [CrossRef] [PubMed]
  64. Ugbenyen, A.; Cosa, S.; Mabinya, L.; Okoh, A. Bioflocculant production by Bacillus sp. Gilbert isolated from a marine environment in South Africa. Appl. Biochem. Microbiol. 2014, 50, 49–54. [Google Scholar] [CrossRef]
  65. Richardson, P.F.; Connelly, L.J. Industrial coagulants and flocculants. In Reagents in Mineral Technology; Routledge: London, UK, 2018; pp. 519–558. [Google Scholar]
  66. Pu, S.; Ma, H.; Deng, D.; Xue, S.; Zhu, R.; Zhou, Y.; Xiong, X. Isolation, identification, and characterization of an Aspergillus niger bioflocculant-producing strain using potato starch wastewater as nutrilite and its application. PLoS ONE 2018, 13, e0190236. [Google Scholar] [CrossRef]
  67. Pu, S.-Y.; Qin, L.-L.; Che, J.-P.; Zhang, B.-R.; Xu, M. Preparation and application of a novel bioflocculant by two strains of Rhizopus sp. using potato starch wastewater as nutrilite. Bioresour. Technol. 2014, 162, 184–191. [Google Scholar] [CrossRef] [PubMed]
  68. Li, Y.; Xu, Y.; Liu, L.; Jiang, X.; Zhang, K.; Zheng, T.; Wang, H. First evidence of bioflocculant from Shinella albus with flocculation activity on harvesting of Chlorella vulgaris biomass. Bioresour. Technol. 2016, 218, 807–815. [Google Scholar] [CrossRef]
  69. Satyanarayana, K.; Guimarães, J.; Wypych, F. Studies on lignocellulosic fibers of Brazil. Part I: Source, production, morphology, properties and applications. Compos. Part A Appl. Sci. Manuf. 2007, 38, 1694–1709. [Google Scholar] [CrossRef]
Microbiolres 12 00070 g001 550
Figure 1. The effect of inoculum size on bioflocculant production. Different letters (a,b) signify statistical significance at (p < 0.05).
Figure 1. The effect of inoculum size on bioflocculant production. Different letters (a,b) signify statistical significance at (p < 0.05).
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Microbiolres 12 00070 g002 550
Figure 2. Effect of time course on flocculating activity, fungal growth, and pH.
Figure 2. Effect of time course on flocculating activity, fungal growth, and pH.
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Figure 3. Infrared spectrum of the purified bioflocculant.
Figure 3. Infrared spectrum of the purified bioflocculant.
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Figure 4. X-ray diffraction of the purified bioflocculant.
Figure 4. X-ray diffraction of the purified bioflocculant.
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Figure 5. Scanning micrograph of the bioflocculant (a), kaolin particles (b), and flocculated kaolin particles (c).
Figure 5. Scanning micrograph of the bioflocculant (a), kaolin particles (b), and flocculated kaolin particles (c).
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Table
Table 1. Effect carbon and nitrogen sources, speed, temperature, cation, and pH on flocculation.
Table 1. Effect carbon and nitrogen sources, speed, temperature, cation, and pH on flocculation.
Carbon SourceFA (%) ± SDNitrogen SourceFA (%) ± SDSpeed (rpm)FA (%) ± SDTemperature (°C)FA (%) ± SDCationsFA (%) ± SDpHFA (%) ± SD
Sucrose79.3 ± 1.79 aCasein78 ± 0.41 a6067.3 ± 0.94 a2069.3 ± 0.47 aMnCl2+78.3 ±10.27 a353.4 ± 0.04 a
Lactose81.4 ± 0.49 a(NH4)2SO480 ± 0.49 a8071.3 ± 2.62 a2571.7 ± 3.09 aAlCl3+74.3 ± 1.25 a456.4 ± 0.05 a
Maltose87.3 ± 4.58 aPeptone94 ± 0.31 b10071.7 ± 4.50 a3086 ± 12.96 aFeCl3+73.0 ± 2.49 a556.7 ± 0.17 a
Glucose92.2 ± 1.85 abNH4NO372 ± 0.54 ab12095.3 ± 2.87 b3597 ± 0.82 aK+73.3 ± 0.94 a669.2 ± 0.15 a
Starch82.3 ± 2.36 abYeast extract87 ± 0.31 abc14096.0 ± 2.05 b4086.7 ± 0.47 aLi+73.3 ± 3.30 a791.1 ± 0.13 ab
Xylose75.3 ± 2.49 aUrea72 ± 0.54 ab16095.3 ± 2.87 b4582.7 ± 11.59 aBa2+84.0 ± 2.05 a889.2± 0.17 ab
Galactose81 ± 2.16 ab 18076.3 ± 3.09 a5078 ± 14.97 aNa+95.0 ± 2.5 ab991.3 ± 1.9 ab
Control36 ± 2.73 c1069.0 ± 0.4 a
1177.2 ± 0.3 ab
1268.2 ± 0.17 a
FA denotes flocculating activity while SD represents standard deviation. Different letters (a–d) signify statistical significance at (p < 0.05).
Table
Table 2. Effect of dosage, temperature, pH, and salinity on flocculating activity of a purified bioflocculant.
Table 2. Effect of dosage, temperature, pH, and salinity on flocculating activity of a purified bioflocculant.
Dosage Size (mg/mL)FA (%) ± SDTemperature (°C)FA (%) ± SDpHFA (%) ± SDSalinity (g/L)FA (%)
0.254.4 ± 2.79 a5079.9 ± 2.60 a348.0 ± 7.30 a581.2 ± 3.13 a
0.480.2 ± 2.81 b6076.8 ± 3.57 a448.0 ± 4.01 a1075.0 ± 1.24 a
0.659.4 ± 3.04 a7071.3 ± 3.71 a536.4 ± 4.38 a1561.1 ± 3.54 ab
0.850.8 ± 0.65 a8068.3 ± 2.05 a657.3 ± 3.0 ab2057.0 ± 2.86 b
1.028.4 ± 3.89 ab9065.5 ± 2.48 a767 ± 3.37 b2550.3 ± 5.85 b
10067.57 ± 1.82 a869.1 ± 1.06 b3040.4 ± 5.59 ab
12164.5 ± 0.41 a965.0 ± 3.23 ab
1058.0 ± 5.57 a
1153.3 ± 1.74 a
12 49.1 ± 2.39 a
FA denotes flocculating activity, whereas SD denotes standard deviation. Different letters (a,b) denote statistical significance at (p < 0.05).
Table
Table 3. Characteristics of bioflocculant from P. kudriavzevii MH545982.1 vs. bioflocculant from other fungi.
Table 3. Characteristics of bioflocculant from P. kudriavzevii MH545982.1 vs. bioflocculant from other fungi.
Bioflocculant ProducersDosageFA (%)pHFA (%)TemperatureFA (%)Citation
P. kudriavzevii MH545928.10.4 mg/mL80.2%880.2%50 °C79.9%Present study
Aspergillus flavus0.2 mg/mL 7 35 °C David et al. [32]
Aspergillus niger0.4 mg/mL 779.0%40 °C68.4%Richards and Connelly [65]
Asperillus oryzae3.2 g/L91.1%591.1%60 °C Nie et al. [25]
Aspergillus niger (A18)5 mL/L90.1%690.1%100 °C83%Pu et al. [66]
Zryzopus sp.0.1 mg/mL85%583%30 °C95%Pu et al. [67]
FA denotes flocculating activity.
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Tsilo, P.H.; Basson, A.K.; Ntombela, Z.G.; Maliehe, T.S.; Pullabhotla, R.V.S.R. Isolation and Optimization of Culture Conditions of a Bioflocculant-Producing Fungi from Kombucha Tea SCOBY. Microbiol. Res. 2021, 12, 950-966. https://doi.org/10.3390/microbiolres12040070

AMA Style

Tsilo PH, Basson AK, Ntombela ZG, Maliehe TS, Pullabhotla RVSR. Isolation and Optimization of Culture Conditions of a Bioflocculant-Producing Fungi from Kombucha Tea SCOBY. Microbiology Research. 2021; 12(4):950-966. https://doi.org/10.3390/microbiolres12040070

Chicago/Turabian Style

Tsilo, Phakamani H., Albertus K. Basson, Zuzingcebo G. Ntombela, Tsolanku S. Maliehe, and Rajasekhar V. S. R. Pullabhotla. 2021. "Isolation and Optimization of Culture Conditions of a Bioflocculant-Producing Fungi from Kombucha Tea SCOBY" Microbiology Research 12, no. 4: 950-966. https://doi.org/10.3390/microbiolres12040070

APA Style

Tsilo, P. H., Basson, A. K., Ntombela, Z. G., Maliehe, T. S., & Pullabhotla, R. V. S. R. (2021). Isolation and Optimization of Culture Conditions of a Bioflocculant-Producing Fungi from Kombucha Tea SCOBY. Microbiology Research, 12(4), 950-966. https://doi.org/10.3390/microbiolres12040070

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