Journal of Innovations in Pharmaceutical and Biological Sciences (JIPBS)
eISSN: 2349-2759 | pISSN: 2395-1095 | Vol. 4, Issue 3, 2017, pp. 55-66

Batch and fed-batch production of polyhydroxyalkanoates from sugarcane molasses by Bacillus flexus Azu-A2

Said El-Sayed Desouky1, Mohamed Ali Abdel-Rahman1, Mohamed Salah Azab1, Mahmoud E. Esmael1

1Botany and Microbiology Department, Faculty of Science (Boys), Al-Azhar University, P.N.:11884, Nasr City, Cairo, Egypt
DOI: 10.56511/JIPBS.2017.v4.i03.pp55-66 | Published: 2017-07-05 | Article page and PDF

Abstract

Production of bioplastic has recently attracted great interest as an environmentally friendly alternative to petrochemical plastics. The present study aimed at production of polyhydroxyalkanoates (PHAs), a biodegradable thermoplastic, from agro-industrial wastes by potent bacterial isolates. Ninety-six isolates were obtained from different localities in Egypt and assayed for qualitative and quantitative production of PHA using sugarcane molasses. Bacterial isolate AZU-A2 showed the highest production of PHA. This strain was identified as Bacillus flexus strain AZU-A2 by 16S rRNA gene sequence and biochemical characterization. Physiological and nutritional factors affecting PHA production were optimized in batch fermentations. Agitation rate, supplementation of acetic acid as an auxiliary carbon source, and ammonium chloride as nitrogen source were critical factors affecting fermentation of PHA production. Maximum production of 3.97 g/L PHA with recovery yield of 88.0 (%, w/w) was achieved after 24h in batch fermentation in optimized medium. A maximal PHA production of 6.13 g/L at recovery yield of 92.1 (%, w/w) was obtained in fed-batch fermentation. The characteristics of extracted PHA were analyzed using 1H-NMR, 13C-NMR and FTIR spectroscopy techniques.

Keywords: Bioplastic; PHA-production; Fed-batch fermentation; Bacillus flexus

Introduction

The accumulation of synthetic plastics has become a major environmental problem due to their low biodegradation, therefore, production of biodegradable plastic materials as an alternative to synthetic plastics has become urgent in recent years. Polyhydroxy-alkanoates (PHAs), bio-based polymers, have received a great attention due to their inherent biodegradability, sustainability and environmentfriendly properties beside its physical and mechanical properties that resemble those of petrochemical thermoplastics [1-4]. It has several applications including packaging, moulded goods, paper coatings, nonwoven fabrics, adhesives, films and performance additives [5].

PHAs are biogenic polyesters that can be naturally accumulated in bacterial cultures as hydrophobic inclusions of carbon and energy storage compounds under limiting nutrients in the presence of excess carbon source [6]. The property of PHA depends on their chemical composition (homo-or co-polyester, contained hydroxyl fatty acids) [5].

Structurally, PHAs are consisting of different monomers with straight, branched, saturated, unsaturated and also aromatic structures. According to monomer size, PHA can be classified into short chain length with 5 or less carbon atom in a monomer, and medium chain length with 3-14 The market consumption of PHA is estimated to be 34,000 MT in 2018. Currently, the market for PHA is projected to grow annually at a CAGR of 4.88% that is valued to reach USD 93.5 Million by 2021 (http://www.marketsand markets.com). These rising demands are attracting to increase the production capacities to be competitive with synthetic plastics. To meet the worldwide requirements for PHA and to be commercially viable, overall production costs should be reduced. This can be achieved by using less expensive substrate or waste materials because the primary cost is mainly depending on the huge amount of carbon source required for the fermentative production. Another method that reduces the PHA cost is to improve the production, productivity and yield of PHA fermentation. Seventy percent of global sugar comes from sugarcane where its current annual production of 1.89 billion tones as fresh cane [8]. It is estimated that from everyone hundred tons of sugarcane crushed in a factory, about 11 tons of sugars are produced and 3 tons of molasses can be recovered as non-food by-product raw waste of sugar industry [9]. Molasses contains plenty of sugars, up to 50% sucrose, and other nutrients including organic acids, vitamins and minerals [10]. The nitrogen content of cane molasses is very low at about 0.5–0.9% (w/v). These characteristics make these wastes materials are suitable for PHA-producing bacteria achieving high cell density with high PHA production [11].

Therefore, the present study aimed to isolate and screen novel PHA-producing bacteria from environmental sources having ability to produce PHA from sugarcane molasses. We also aimed to optimize the PHA production in different fermentation modes. Finally, the characterization of the extracted PHA will be analyzed.

Experimental

Materials and Methods

Isolation sources and medium

Isolation sources were collected from different localities in Egypt as follows: solid samples include soils collected from field, gas station, factory of leather production, paint factory, and wastes from vegetable processing company. Liquid samples include, oil contaminated water, sewage contaminated water and sea water and molasses. Enrichment medium for bacterial isolation consist of (g/L)[12]; Na HPO , 9.0; KH PO , 1.5; MgSO .7H O, 0.2; NH Cl, 1.0; CaCl .2H O, 0.02; Fe(III)NH -Citrate, 0.0012; and 1ml of 2 2 4 trace elements solution containing (g/L): EDTA, 50.0; FeCl 3, 8.3; ZnCl , 0.84; CuCl .2H O, 0.13; CoCl .6H O, 0.1; MnCl .6H O, 0.016; H BO , 0.1. Glucose was 2 2 3 4 supplemented at 20 g/L as sole carbon source. The pH of the medium was adjusted to 7.0 using 1 N NaOH and 1 N HCl.

Screening tests for PHA-producing isolates

Primary screening of PHA-producing microorganisms was done by viable-colony staining method using Nile Red stain as follows: 0.5 μg Nile Red /mL of solid medium was prepared, sterilized and poured into Petri plates. The obtained isolates were streaked on agar plates and incubated o at 37 C for 3 days then examined under UV light. The lighted colonies were recorded as positive [13].

For secondary screening, selected bacterial isolates were cultivated in mineral salt medium supplemented with 2% glucose or molasses separately. The media were incubated o for 72 h at 37 C and 150 rpm. The polymers were extracted and quantified.

Identification of selected isolate

Morphological, physiological and biochemical properties of the most potent isolate AZU-A2 were examined as described by Abdel-Rahman [14]. Then the identity of bacterial isolate was confirmed based on 16s rDNA sequence analysis. Genomic DNA was extracted, then 16S rRNA was amplified in PCR using the genomic DNA as template and two bacterial universal primers, 27f (5- GAGTTTGATCACTGGCTCAG-3) and 1492r (5- TACGGCTACCTTGTTACGACTT-3) as described by Abdel-Rahamn,[14]. The PCR products were sequenced by Sigma Company (Egypt) using ABI 3730xl DNA sequencer with the two primers. The 16S rRNA sequence was compared with GenBank database using the NCBI BLAST program. Multiple sequence alignment was done using ClustalX 1.8 software package and a phylogenetic tree was constructed by the neighbor joining method using MEGA (Version 6.1) software. The confidence level of each branch (1,000 repeats) was tested by bootstrap analysis.

Factors affecting PHA production

The following factors were examined for their effect on PHA production by the most potent bacterial isolate. The deduced optimal conditions resulted from each experiment was taken in consideration in the next experiment.

For optimal molasses concentration, different concentrations of molasses were applied (viz., 0.5, 1, 2, 3, 4, 5 and 10 %) to production media. Strain AZU-A2 was inoculated at 10 % (v/v) in 250 mL Erlenmeyer flask containing 50 ml mineral o salt medium (MSM), and incubated at 37 C and 150 rpm. Samples were withdrawn periodically and analyzed for DCW, PHA production and residual sugar.

To study the optimal nitrogen source; ammonium chloride in the basal MSM-molasses medium was replaced at equimolecular weight with organic (peptone and yeast), or inorganic (ammonium chloride, ammonium sulphate, sodium nitrate and di-ammonium hydrogen orthophosphate) nitrogen sources, separately. Fermentation media was supplemented with 3% molasses as sole carbon sources. The strain was inoculated at 10 % (v/v) as described previously o and incubated at 37 C and 150 rpm. All the previous optimal conditions were applied. Samples were withdrawn periodically and analyzed for DCW, PHA production and residual sugar as mentioned before.

To determine optimal ammonium chloride concentration, different concentrations of ammonium chloride viz., 0.5, 1, 1.5, 2, 2.5, 3 and 4g/L were supplemented to basal MSM- molasses and sterilized. Strain was inoculated at 10 % (v/v) o and incubated at 37 C and 150 rpm for 36h. Samples were withdrawn periodically and analyzed for DCW, PHA production and residual sugar as mentioned before.

To determine optimal pH value, different fermentation media were prepared at various initial pH values viz., 5, 6, 6.5, 7, 7.5, 8, and 9 were used without pH control during fermentation. These media were filter sterilized. After inoculation of strain AZU-A2 at 6 % (v/v), the media were o incubated at 37 C and 150 rpm for 36h. Samples were withdrawn periodically and analyzed for DCW, PHA production and residual sugar as mentioned before.

To investigate the effect of phosphorus, Na HPO and 2 4 KH PO were supplemented to the fermentation media at 2 4 various ratio of 12.0:2.0, 9.0:1.5, 6.0:1.0, 3.0:0.5, 1.0:0.25 g/l. Strain AZU-A2 was inoculated at 6 % (v/v), the media o were incubated at 37 C and 150 rpm for 36 h. Samples were withdrawn at different time intervals and analyzed for DCW, PHA content and residual sugars as mentioned above.

To investigate the optimal agitation speed, fermentation optimized before. Then inoculated and incubated at different agitationrates viz., 0 (static), 50,150, 200 and 250 rpm. After incubations, DCW, PHA and sugar were analyzed as previously mentioned.

To study the effect of addition of co-substrates (auxiliary carbon sources), methanol, ethanol, sodium acetate, acetic acid, sodium citrate, olive oil, corn oil, paraffin oil, sesame oil and soy oil were supplemented separately at 0.5% to the previously optimized MSM-molasse (3%) media. Media o were inoculated at 6 % and incubated at 37 C and 200 rpm. At the end of each incubation period DCW, PHA, and the residual sugar were estimated.

To study the optimal concentration of acetic acid, different concentrations at 0.25, 0.5, 0.75, 1, 2, 3, 5 % were supplemented to the optimized cultivation MSM-molasses media. Inoculation of strain and incubation was performed as previous experiment.

Fed-batch fermentation

Fed batch fermentations were carried out in 250 ml Erlenmeyer flask with optimized MSM- molasses (3%, w/v), with acetic acid (1%, v/v) and ammonium chloride at o concentration (0.2%, w/v) and incubated at 37 C and 200 rpm. pH was adjusted to 7.5 during fermentation. Feedings were supplemented with different strategies (different feeding at various times). First, feeding was performed after 24 h either by addition of sugarcane molasses at 3% (w/v) [fed batch A] or sugarcane molasses at 3% (w/v) plus ammonium chloride at 0.15 % (w/v) [fed batch B]. Second, feeding was carried out after 12h with sugarcane molasses at 1.5 % (w/v) plus ammonium chloride at 0.075 % (w/v) [fed batch C] or sugarcane molasses at 1.5 % (w/v) plus ammonium chloride at 0.075 % (w/v) plus phosphorus at 0.35% (w/v) [fed batch D]. The feeding was done as the residual sugar concentration decreased below 8 g/L.

Analytical methods

Cell growth was monitored by measuring the optical density at 600 nm using spectrophotometer (M-ETKAL-721 Spectrophotometer). Culture medium was centrifuged at 10,000 rpm, at 4°C for 5 min and the cell pellet was washed with distilled water. The cell pellet was harvested by centrifugation and dried at 105°C overnight till constant weight was obtained. Cell mass concentration was determined by the standard calibration curve between OD600 and cell dry weight.

PHA extraction: After incubation period, bacterial cells were harvested by centrifugation at 10000 rpm for 10 minutes. The pellet was then treated with sodium hypochlorite solution (4% w/v) and incubated at 37°C for 1 h and again centrifuged at 5000 rpm for 15 min, the supernatant was discarded and the pellet was then washed with distilled water, acetone for washing and extraction, respectively. After washing, the pellet was dissolved in 5 mL of boiling chloroform and allowed to evaporate.

PHA Assay After evaporation, PHB extracted was subjected to spectrophotometric analysis by Dekwer et al., [41] method. Sample containing PHB polymer in chloroform was transferred to a clean test tube, allowing chloroform to evaporate and 10 ml of concentrated H SO was added. The 2 4 tube is capped with a glass marble and heated for 10 min at 100 °C in a water bath. After cooling, the solution was transferred to a silica cuvette and the absorbance at 235 nm was measured against a sulfuric acid blank using UV Spectrophotometric (JENWAY 6305 Spectrophotometer). Standard curve was established with PHB concentrations ranging from 0.5-3.5 mg /ml.

Sugar concentration was assayed using the phenol sulphuric acid methods as described by Dubois, et al., [42].

Fermentation kinetics

Production kinetics of PHA and CDW were studied by calculating the product yield of PHA with respect to sugar consumption Y (g/g), the product yield of PHA with P/S respect to biomass Y (g/g), biomass yield related to sugar P/X consumption Y (g/g) and productivity of PHA per h X/S (g/L/h) of the culture media.

Characterization of PHA

Transform-Infrared Spectroscopy (FTIR):

The chemical structure of the extracted PHA was analyzed by Fourier transform infrared spectroscopy at Faculty of pharmacy, Al-Azhar University, Cairo, Egypt. The biopolymer was dissolved in chloroform and added to KBr pellets and then the solvent was evaporated. The infrared spectra of the samples were recorded in the wave number −1 range from 500 to 4000 cm using a Perkin Elmer Fourier transform infrared (FTIR) spectrophotometer (NICOLET-IR 200) using KBr disc [15].

NMR spectroscopy for PHA analysis

1 Mercury 400 NMR spectrometer was used for 400-MHz H 13 NMR, and C NMR. NMR spectra were recorded from a CDCl3 solution of the PHA (30 mg/ml) at 20°C, 1.30809856s acquisition times and 12.5250501 kHz spectral 13 width. C-NMR spectra were recorded from a CDCl 3 1 solution of the samples, using H decoupling, 0.83361792s 1 acquisition time and 39.3081761 KHz spectral width. H- 13 NMR and C-NMR chemical shifts were referred to CHCl3 and CDCl3 with c = 5.0 ppm and c = 100.0 ppm, respectively.

Results and Discussion

Results

Isolation and screening of PHA-producers from different sources

Several solid and liquid samples collected from different localities in Egypt were used for isolation of PHA-producing isolates using enrichment media containing glucose as described in materials and methods. Ninety-six bacterial isolates were obtained and purified. These isolates were preliminary screened for evaluation PHA production through fluorescence using Nile red staining assay technique. Out of these isolates, 14 isolate showed bright fluorescence on agar plates upon exposing to UV light at wavelength at 312 nm. This indicate that these isolates are primarily able to produce PHA from glucose, therefore, selected for further quantification screening.

The selected isolates (14 isolates) were cultivated in mineral salt media supplemented with glucose and incubated for 72 o h at 37 C. Cell growth was examined. Then the cells were collected for PHA extraction. PHA content was estimated and compared. Eight isolates showed PHA production ranged 0.2-0.48 g/L, 5 isolates produced PHA at range 0.570-0.930 g/L, whereas only one isolate produced 1.18 g/L of PHA as shown in Table (1).

Those isolates were also investigated for PHA production from molasses. As shown in Table (1), six isolates couldn’t utilize molasses, whereas 3 isolates produced less PHA at 0.220-0.460 g/L. On the other hand, 5 strains showed increased production with a maximum PHA concentration of 0.790 g/L by isolate AZU-A2. This isolate also produced high PHA concentration from glucose at 0.880 g/L. Therefore, this strain was considered as the most potent isolate and used in further studies for identification and enhancement of PHA production.

Table 1. Quantitative screening test by 14 bacterial isolates for PHA production using 20 g/L of glucose and sugarcane molasses No. Isolates PHA(g/L) ±SD from:
Table 1. Quantitative screening test by 14 bacterial isolates for PHA production using 20 g/L of glucose and sugarcane molasses No. Isolates PHA(g/L) ±SD from:

Isolate AZU-A2 was isolated from soil of leather production factory. Identification of isolate AZU-A2 was performed by studying its morphological (Gram’s reaction, shape), biochemical and genetic characteristics (16S rRNA gene sequence) as shown in Table (2). The strain AZU-A2 is Gram-positive with rod shape, and was catalase-positive, It can grow in media with high salt concentration [up to 10 % sodium chloride]. The isolate showed capability of cellulose, gelatin and starch hydrolysis. However, it could not utilize citrate, pectin, or urea. This isolate could ferment different sugars including glucose, xylose, galactose, maltose, fructose, mannitol, sucrose, and lactose but not able to ferment inositol, myo-inositol, cellobiose, or inulin.

The16S rRNA gene sequence of the AZU-A2 isolate showed the highest similarity at 99. %with Bacillus flexus strain AUCAB18 [GenBank accession NO.: GU297608.1], and Bacillus flexus strain S2 [GenBank accession NO. KX242400.1] The phylogenetic tree constructed using strain AZU-A2 and other closely related type strains is depicted in Figure (1). The phylogenetic tree showed that strain AZU- A2 clustered with Bacillus flexus with 100 % bootstrap support. Therefore, we described the newly isolated strain as Bacillus flexus strain AZU-A2.

Table 2. A summary of the morphological, physiological and biochemical characteristics of the most potent bacterial isolate AZU-A2 Test Result Test Result
Table 2. A summary of the morphological, physiological and biochemical characteristics of the most potent bacterial isolate AZU-A2 Test Result Test Result
Figure 1. Phylogenetic analysis of 16S rRNA sequences of the bacterial isolates (AZU-A2) with the sequences from NCBI. Symbol ■ refers to 16S rRNA gene fragments retrieved from this study. The analysis was conducted with
Figure 1. Phylogenetic analysis of 16S rRNA sequences of the bacterial isolates (AZU-A2) with the sequences from NCBI. Symbol ■ refers to 16S rRNA gene fragments retrieved from this study. The analysis was conducted with

Consumes sugar (g/L)

Table 3. Effect of different nitrogen sources on PHA production from sugar-cane molasses by Bacillus felxus AZU-A2
Table 3. Effect of different nitrogen sources on PHA production from sugar-cane molasses by Bacillus felxus AZU-A2

Factors affecting PHA production

Effect of molasses concentrations

In order to investigate the influence of molasses concentrations on DCW and PHA production, strain AZU- o A2 was cultivated in MSM medium at 37 C and pH7 with initial concentration of molasses range from (0.5-10%).As shown in Figure (2A), DCW was increased with increasing molasses concentration from 0.5 % up to 4% at 1.67 g/L and 3.87 g/L, respectively. Same DCW of 3.87 g/L was obtained at molasses concentration of 4.0-10.0 %. The highest PHA recovery yield of 36.1 (w/w) % was obtained with 3% molasses achieving the highest PHA production of 1.38 g/L with yield of 0.126 g/g-consumed sugar and low PHA productivity of 0.038 g/L/h (Figure 2B). From the above results, concentration 3% of molasses were considered as the

Figure 2. Effect of different concentrations of molasses on (A) cell growth (Dry cell weight), sugar consumption, PHA production; (B) PHA yield, productivity and recovery by strains AZU-A2 in batch fermentations.
Figure 2. Effect of different concentrations of molasses on (A) cell growth (Dry cell weight), sugar consumption, PHA production; (B) PHA yield, productivity and recovery by strains AZU-A2 in batch fermentations.

Optimization of nitrogen source

Limited nitrogen condition is one of the critical factors affecting cell growth and PHA synthesis. The effect of some organic and inorganic nitrogen sources were investigated in PHA fermentation by strain AZU-A2 in MSM medium with o 3 % molasses at 37 C as shown in Table (3). Cell growth was increased with fermentation time achieving maximum value of 3.75 g/L at 36 h using ammonium chloride. Although comparable DCW (ranged 3.02-4.64 g/L) was obtained from other nitrogen sources, the highest recovery yield at 42.40 (%, w/w) was obtained using ammonium chloride. The highest biomass yield based on substrate (Y ) x/s of 0.824 g/g was obtained after 12 h in a medium supplemented with sodium nitrate but a very low recovery yield and PHA concentration were obtained at 11.49 % and 0.35 g/L, respectively. Peptone, yeast extract, and ammonium dihydrogen orthophosphate achieved lower PHA recovery, titer and productivity than obtained using ammonium chloride (Table 3). A maximum PHA production of 1.59 g/L at yield of 0.144 g/g-consumed sugar was obtained using ammonium chloride as nitrogen source. To determine the optimal concentration of ammonium chloride, batch fermentations were conducted using various concentrations (0.5-4 g/L) as recorded in Table (4). Maximum DCW of 4.35g/L was obtained when ammonium chloride raised up to 4 g/L at 36h. On the other hand, the maximum PHA production 1.84 g/L, recovery yield of 44.86 g/L, and productivity of 0.069 g/L/h were obtained with 1.5 g/L of ammonium chloride after 36h. At this concentration, the PHA yield based on substrate consumed was 0.137 g/g-consumed sugar that is little lower than those obtained with higher ammonium chloride ˃ 1.5 g/L. As a result, 1.5 g/L was selected as the optimal concentration for achieving high efficiency PHA production.

Table 4. Effect of ammonium chloride concentration on PHA production from sugar-cane molasses by Bacillus felxus AZU- A2
Table 4. Effect of ammonium chloride concentration on PHA production from sugar-cane molasses by Bacillus felxus AZU- A2

The influences of pH on growth and PHA accumulation by strains AZU-A2 was investigated by adjusting initial pH at different values (ranged pH 5.0-9.0) using the previously optimized conditions during fermentation.

As shown in Figure 3a, the DCW is almost comparable at a wide range of pH values (6.0-9.0) that ranged 4.02-4.49 g/L after 36 h with almost similar values obtained after 24 h (ranged 4.01-4.38 g/L). A drastic decrease in DCW was obtained at an initial pH 5 at 0.66 g/L. On the other hand, an obvious increase in the PHA production, recovery yield and productivity with an increase in initial pH value achieving their maximum values at pH 7.5 with 2.04 g/L and 46.4 (%, w/w), and 0.057 g/L/h, respectively (Figure 3 B and C). At this value, the PHA based on consumed substrate was 0.184 g/g (Figure 3C). pH controlled fermentations were also conducted, however, lower PHA production (Max. 1.71 g/L) was obtained compared to fermentations with uncontrolled pH (2.04 g/L)[Data not shown]. As result, initial pH 7.5 was considered as the best pH for achieving high efficiency fermentation of PHA by strain AZU-A2.

Effect of phosphorus sources

The influence of different concentrations of phosphorus sources, Na HPO 12H O (range; 1.0-12.0 g/L): KH PO (range; 0.16-1.0 g/L) at ration of 6:1, were investigated on the growth and PHA production by strain AZU-A2. An increased cell growth was obtained with high phosphorus content (total ≥ 3.5 g/L) that ranged 4.24-4.38 g/L compared to 3.81 g/L at phosphorus concentration of 1.16. PHA fermentation efficiency was improved with an increase of phosphorus concentration up to 7.0 g/L [Na HPO 12H O 2 4 2 (6.0 g/L):KH PO (1.0 g/L)] (Table 5). At this concentration, 2 4 a maximum biomass yield Y (0.377 g/g), PHA recovery x/s yield (47.19 %, w/w), PHA production (2.02 g/L), PHA yield (0.178 g/g), and productivity (0.056 g/L/h) were obtained. Therefore, total phosphorus concentration of 7 g/L was considered as the best conditions for achieving high PHA fermentation efficiency within 36 h.

Figure 3. Effect of initial pH value on PHA fermentation from sugar-cane molasses by Bacillus felxus AZU-A2. (A) dry cell weight, (B) PHA production, g/L, and (C) PHA yield, productivity and recovery.
Figure 3. Effect of initial pH value on PHA fermentation from sugar-cane molasses by Bacillus felxus AZU-A2. (A) dry cell weight, (B) PHA production, g/L, and (C) PHA yield, productivity and recovery.
Table 5. Effect of different concentrations of phosphorus sources on PHA production from sugar-cane molasses by Bacillus felxus AZU-A2.
Table 5. Effect of different concentrations of phosphorus sources on PHA production from sugar-cane molasses by Bacillus felxus AZU-A2.
Figure 4. Effect of different agitation rates on cell growth (dry cell weight), sugar consumption and PHA production from sugar-cane molasses by Bacillus felxus AZU-A2. (a) fermentation at static condition, 0 rpm; (b) fermentation at 50 rpm; (c) fermentation at 150 rpm ; (d) fermentation at 200 rpm ; (e) fermentation at 250 rpm. Symbols;▲, Consumed sugar (g/L); ■, PHA concentration (g/L); ♦, DCW (g/L).
Figure 4. Effect of different agitation rates on cell growth (dry cell weight), sugar consumption and PHA production from sugar-cane molasses by Bacillus felxus AZU-A2. (a) fermentation at static condition, 0 rpm; (b) fermentation at 50 rpm; (c) fermentation at 150 rpm ; (d) fermentation at 200 rpm ; (e) fermentation at 250 rpm. Symbols;▲, Consumed sugar (g/L); ■, PHA concentration (g/L); ♦, DCW (g/L).

agitation rate and efficiency of PHA fermentation by strain AZU-A2. Static condition achieved the lowest cell biomass (1.41 g/L) and fermentation kinetic parameters (PHA conc., 0.2 g/L; recovery yield, 14.1 % (w/w); Y , 0.013 g/g; and p/s productivity, 0.003 g/L/h). However, cell biomass, sugar consumption, and PHA production were increased with an increase of agitation speed up to 200 rpm. The highest DCW of 4.39 g/L with highest PHA concentration of 3.0 g/L were obtained after 24 h at an agitation rate of 200 rpm. Also, the

Effect of auxiliary carbon sources (co-substrates)

To improve PHA production by AZU-A2, different additional carbon sources substrates were supplemented separately at concentration of 0.5% to MSM media containing molasses (3%). PHA production was investigated o at different time intervals at 37 C and agitation rate of 200 rpm as shown in Table (6).

Table 6. Effect of different auxiliary carbon sources on PHA production from sugar-cane molasses by Bacillus felxus AZU- A2
Table 6. Effect of different auxiliary carbon sources on PHA production from sugar-cane molasses by Bacillus felxus AZU- A2

3.38 g/L using acetic acid as an auxiliary carbon source. As result, acetic acid and sodium acetate considered as the best auxiliary carbon sources for achieving high efficiency

Figure 5. Effect of different acetic acid concentrations on cell growth (dry cell weight), PHA recovery yield, and PHA production from sugar-cane molasses by Bacillus felxus AZU-A2.
Figure 5. Effect of different acetic acid concentrations on cell growth (dry cell weight), PHA recovery yield, and PHA production from sugar-cane molasses by Bacillus felxus AZU-A2.

Fed-batch fermentation

In order to further enhance cell biomass and PHA production by strain AZU-A2, fed batch fermentation using different feedings were performed. The fermentations were initially started with components of the optimized medium. Different feeding solutions were applied at different time intervals based on its content [either molasses only or molasses mixed with nitrogen and/or phosphorus source; Fed-batch A, b, C, or D as indicated in Material and Methods].

As shown in Figure (6), in fed batch A, where the feeding with molasses only (3%), cell biomass reached 5.50 g/L after 24 with an increase after than achieving its maximal value of 7.07 g/L after 96 h. On the other hand, the accumulation of PHA was increased achieving its maximum value of 5.96 g/L with recovery yield of 84.3 % (w/w) at 96 h. Conducting similar fermentation with feeding solution of molasses and ammonium chloride (Fed-batch B) have resulted in almost similar DCW of 7.17 g/L after 96 h, however, higher accumulation of PHA was obtained achieving its maximal value of 6.13 g/L with recovery yield of 92.12 % (w/w) after 72 h. In another strategy using lower sugar concentration feeding, fed-bach C and D were conducted. In those fermentations, feeding was intermitted supplied to maintain sugar concentration at same level. However, none of those fermentations supported high PHA production than previous even with supplementations with extra nitrogen or phosphorus sources. The maximal PHA produced from fed-batch C and D were 5.05 g/L and 4.31 g/L after 36 h and 48 h, respectively that is lower than obtained in fed-batch A and B. Furthermore, although fed batch A and B achieved higher PHA production than obtained in batch fermentation, the high amount of molasses amount required and fermentation time retard this process.

-1

Figure 7, showed absorption bands at 3453 cm (OH -1 -1 stretching), 2980 cm (C-H stretching), 1736 cm (C=O -1
Figure 7, showed absorption bands at 3453 cm (OH -1 -1 stretching), 2980 cm (C-H stretching), 1736 cm (C=O -1

CDW&PHA (g/l) Residual sugar (g/L) 8 Fed-batch (D) 40 CDW&PHA(g/l) Residual sugar (g/L)

Figure 6. Fed batches fermentation with different feeding for PHA production from sugar-cane molasses by Bacillus 0 felxus AZU-A2 at 37 C, initial pH 7.5 and agitation rate
Figure 6. Fed batches fermentation with different feeding for PHA production from sugar-cane molasses by Bacillus 0 felxus AZU-A2 at 37 C, initial pH 7.5 and agitation rate
Figure 7. Fourier transform infrared spectra analysis of PHA produced by strain AZU-A2
Figure 7. Fourier transform infrared spectra analysis of PHA produced by strain AZU-A2

Nuclear Magnetic Resonance (NMR)

1 H-NMR spectrum of our compound (Figure 8A) indicated characteristic signals of PHA, namely a doublet at 1.31 ppm, which is attributed to the methyl (CH3) group coupled to one proton while a doublet of quadruplet at 2.44 ppm due to the methylene (CH2) group adjacent to an asymmetric carbon atom bearing a single proton. The third signal at 5.21 ppm, which was attributed to the methine (CH) group. This data was matched with the published data for same compound [17]. The values of the chemical shifts as well as the 1 assignments of the H NMR signals, which appeared in the spectra are in agreement with the authentic PHB sample produced from Aldrich Company, which clearly classified the extracted biopolymer from the isolated strain in the present study as poly-3-hydroxybutyric acid and confirmed 13 by C NMR spectrum (Figure 8 B).

1 13

Figure 8. (A) H chemical shifts, (B) C chemical shifts of constituent monomers of purified PHA produced by strain AZU-A2.
Figure 8. (A) H chemical shifts, (B) C chemical shifts of constituent monomers of purified PHA produced by strain AZU-A2.

Discussion

Production of biodegradable and biocompatible green thermoplastics has currently received much attention as an alternative to nonrenewable petroleum derived plastics. PHAs are bio-polyesters materials synthesized by bacteria as intracellular storage material under limited nitrogen condition and excess carbon source. Taking in consideration these conditions, this study aimed to select suitable bacterial strain accumulating high PHA content from inexpensive carbon sources and determining the environmental and nutritional factors that lead to the maximization of PHA production To achieve this aim, 96 bacterial isolates were isolated from different samples collected from Egypt. Bacterial cultures grown on Nile red-containing medium were analyzed under UV to detect hydrophobic compounds inside the cells as previously reported [13, 18]. 14 isolates showed bright to red fluorescence color and used for quantitate analysis of PHA produced from glucose or sugarcane molasses as an o inexpensive carbon source at 37 C for 72 h. Isolate AZU-A2 could accumulate the highest amount of PHA (0.79 g/l) using molasses as substrate and therefore was characterized using biochemical characteristics and genetic 16S rRNA analysis.

In the phylogenetic tree based on the neighbor-joining algorithm (Figure 1), strain AZU-A2 clustered with the members of the genus Bacillus, showing the highest 16S rDNA gene sequence similarity of 99.0% with Bacillus Bacillus flexus strain AZU-A2. Bacillus spp. is a black horse in industry due to their advantages of low nutritional requirements, rapid growth, having machinery enzymes for utilization of several sugars and lacking LPS in Gram positive [19]. Interestingly our isolated strain AZU-A2 could accumulate the highest amount of PHA within 36 h that is very short time compared to previously reported Bacillus strains. Maximum PHB production from molasses was obtained after 72 h by Bacillus flexus ME-77 [19] and Bacillus thuringiensis [20]. Kalaivani and Sukumaran, [21] reported maximum production of PHA from molasses observed after 76 h by Bacillus sp. KSN5.

PHA produced in this study was characterized as polyester by Fourier transform infrared (FTIR) spectroscopy to study the molecular structure [22], and NMR spectroscopy. Due to the Low PHA produced in MSM with molasses at 0.79 g/L, physical and nutritional factors affecting PHA production were optimized in batch fermentations. Sugarcane molasses concentration at 3%; ammonium chloride, 1.5 g/L; phosphorus concentration, (Na HPO .12H O, 6 g/L; 2 4 2 KH PO 1 g/L); acetic acid conc. 1 %; initial pH, 7.5; 2 4, o agitation speed, 200 rpm; and 37 C were the optimal fermentation conditions for PHA production by AZU-A2. Under these conditions, maximum PHA production of 3.97 g/L at recovery yield of 88.0 (%, w/w) were achieved after 24 h in batch fermentation.

The optimal molasses concentration of 3% (w/v) achieved better growth with high recovery yield. The decreased cell growth at higher molasses concentration (˃ 3%) might due to osmotic stress. Several authors also reported that 3% molasses concentration is an optimal for achieving high PHA production from Bacillus spp. [19–20, 23–24]. Sharma and Bajaj, [25] reported that maximum PHB yield was obtained at 2% of molasses by Enterobacter sp. SEL2.

Supplementation of 1.5 g/L ammonium chloride as nitrogen source was positively enhanced the accumulation of PHA by strain AZU-A2 amongst other tested sources. Higher accumulation of PHA inside that cells was obtained at 42 % recovery yield while other tested sources attained only 11– 30 % PHA recovery. It is observed that supplementation of organic nitrogen sources (peptone or yeast extract) and sodium nitrate supported high growth (ranged 3.02-3.62 g/L) but not PHA accumulation that ranged 0.35–0.90 g/L. Ammonium chloride was also reported as the best nitrogen source for PHAs from molasses by Bacillus megaterium [23, 26–27]. Ammonium sulphate supported high growth and PHA production by Rhizobium elnti and Pseudomonas stutzeri [28].

pH is one of the critical factors that affects the cell growth and product formation. Initial pH 7.5 (uncontrolled) was found to be optimum for PHA production by AZU-A2. Most studies reported neutral to slightly acidic or slightly alkaline pH (pH 6.5–8.0) is the optimal for PHAs accumulation by several bacterial [19, 25, 29–30].

Phosphate limited condition is another important factor for production of PHA and maximum recovery yield of PHA was observed at phosphorus concentration (Na HPO 2 4 12H O 6 g/L - KH PO 1 g/L) after 36 h that is higher 2 2 4 requirement than reported by other reported strains [32-33]. Qiu et al., [33] achieved maximum production of PHA using Na HPO 12H O at 3 g/L and KH PO of 0.5 g/L by A. hydrophila 4AK4. Goma, [32] stated that, the maximum production of PHA by B. subtilis and E. coli was recorded in the presence of 2 g/L of KH PO and Na HPO .2H O. Sangkharak and Prasertsan [34] reported a maximum PHB production at phosphorus concentration 0.1 g/L K HPO , 0.1 2 4 g/L KH PO by R. sphaeroides.

2 4 Agitation rate is reported to be a critical factor for PHA accumulation by our strain, AZU-A2. The lowest growth rate was achieved at static condition, while a significant increase in growth rate accompanied by accumulation of PHA was gradually increased by increasing agitation rate up to 200 rpm which might attributed to the increase in oxygen transfer and mass transfer rates and requirement of aerobic condition for Bacillus growth [35]. Beyond this level, higher growth was achieved but accumulation of PHA was significantly decreased that attributed to limitations of stress conditions required for PHA granules storage [36]. Tripathi et al., [29] stated that maximum cell mass and PHB production occurred at an agitation speed of 175 rpm by Pseudomonases aregunoisa NCIM No. 2948.

Supplementation of 1 % acetic acid as an auxiliary carbon source maximized PHA recovery yield of PHA to 88.01% (w/w) by strain AZU-A2. This recovery yield is superior to that obtained by Venkates war et al., [37] who achieved maximum recovery at 63.0 5% using 20 g/L VFA (acetate 19 g/L - propionate 1g/L) by Hydrogenopha gapalleronii. Combinations of acetate with valerate and acetate with propionate were reported to induce the accumulation of poly- β -hydroxybutyrate-co- β -hydroxyvalerate within the cell [38].

In order to avoid or reduce substrate associated osmotic stress and achieve high product concentration, fed-batch fermentation has been conducted. However, studies of fedbatch fermentation on molasses are limited, mainly because of difficulties to determine adequate feeding strategies for control of critical parameters. Therefore, different feeding strategies were applied as shown in result section. Feeding with 3% molasses plus ammonium chloride supported higher cell growth and PHA accumulation as compared to feeding of molasses only achieving maximum recovery of 92.12 % and 84.28%, respectively. While feeding with lower molasses concentrations of 1.5% with nitrogen and/or phosphorus attained lower fermentation efficiency. The maximum PHA production of 6.13 g/L was achieved by feeding 3% molasses plus ammonium chloride that is 54.4 % increase as compared to data obtained in batch fermentation. The results obtained in this study is superior to that obtained by Hamieh et al., [39] who reported an increase in PHB to 27.5% in fed batch fermentation as reported that P(3HB-co-3HV) content reached maximum value of 39.8 wt, % after 54 h in fed-batch fermentation by Yangia sp. Nd199 using molasses.

Conclusion

In the present report, polyhydroxyalkanoates production and optimization using sugarcane molasses as cheap substrate was achieved by a newly isolated Bacillus flexus strain AZU-A2. Sugarcane molasses concentration at 3%; ammonium chloride, 1.5 g/L; phosphorus concentration, (Na HPO .12H O, 6 g/L; KH PO 1 g/L); acetic acid conc.

2 4 2 2 4, o 1 %; initial pH, 7.5; agitation rate, 200 rpm; and 37 C were the optimal fermentation conditions for PHA production. Under these conditions, maximum PHA production of 3.97 g/L at recovery yield of 88.0 (%, w/w) were achieved after 24 h in batch fermentation. Fed batch fermentation resulted in improved PHA production (6.13 g/L) and recovery yield (92.1 % of DCW, w/w). PHA was characterized as polyester by Fourier transform infrared (FTIR) and NMR spectroscopy.

Conflict of interest

All the authors declare that they have no conflicts of interest regarding this paper.

References

References

  1. Anju, A, Zuber M, Mahmood ZK, Noreen A, Naveed A, Tabasum S: Microbial production of polyhydroxyalkanoates and its copolymers, Int. J. Biol. Macromol 2016; 89: 161–174.
  2. Godbole S: A Review on Strategies for Production of (Poly-3- Hydroxyalkanoates): The green materials for sustainable development - current status and future prospects IJSRR 2016; 5(1): 01– 19.
  3. Salehizadeh H, and Loosdrecht MCMV: Production of polyhydroxyalkanoates by mixed culture: recent trends and biotechnological importance. Biotechnol. Adv (2004); 22: 261–279.
  4. Zhu C, Chiu S, James P,Nakas P, Christopher J, and Nomura T C: Bioplastics from waste glycerol derived from biodiesel industry, J. Appl. Poly. Sci 2013;130(1): 1–13
  5. Bugnicourt E, Cinelli P, Lazzeri A, Alvarez V: Polyhydroxyalkanoate: Review of synthesis, characteristics, processing and potential applications in packaging, Express Polymer Lett 2014; 8 (11): 791–808
  6. Muhammadi S, Muhammad A, and Shafqat H: Bacterial polyhydroxyalkanoates-eco-friendly next generation plastic: Production, biocompatibility, biodegradation, physical properties and applications, Green Chem. Lett. and Rev 2015; 8:3-4, 56–77.
  7. TaguchiS, and Doi Y: Evolution of polyhydroxyalkanoate production system by “enzyme evolution”: successful case studies of directed evolution.Macromol. Biosc2004; 4: 145–156.
  8. Pagani V, Stella T, Guarneri T, Finotto G, van den Berg M, Marin FR, Confalonieri R: Forecasting sugarcane yields using agro-climatic indicators and canegro model: A case study in the main production region in Brazil. Agr. Syst 2017; 154: 45–52.
  9. Panda, H: The complete book on sugarcane processing and by-products of molasses (with analysis of sugar, syrup and molasses). Asia Pacific Business Press Inc, New Delhi 2011.
  10. Tripathi AD, Sirvastava SK, and Singh RP: Statistical optimization of phsical process variables for bio plastic production by Alcaligens sp. Biomass and Bioenergy 2013; 55: 243–250.
  11. Jiang G, David JH, Kowalczuk M, Johnston B, Adamus G, Irorere V, and Radecka I: Carbon sources for polyhydroxyalkanoates and an integrated biorefinery. Int. J. Mol. Sci 2016; 17(7): 1157.
  12. Schlegel HG, Kaltwasser H, and Gottschalk G: A submersion method for culture of hydrogen-oxidizing bacteria: growth physiological studies. Arch Mikrobiol 1961; 38:209–222
  13. Spiekermann P, Rehm B, and Kalscheuer R: A sensitive, viable-colony staining method using Nile red for direct screening of bacteria that accumulate polyhydroxyalkanoic acids and other lipid storage compounds. Arch Microbiol 1999; 71:73–80
  14. Abdel-Rahman MA: Establishment of efficient cellulolytic bacterial consortium potential for designed composting of rice straw. Int. J. Adv. Res. Biol. Sci 2016;3(4): 211–228.
  15. Shamala TR, Chandrashekar A, Vijayendra SV, Kshama L: Identification of polyhydroxyalkanoate producing Bacillus spp. using the polymerase chain reaction. J. Appl. Microbiol 2003; 94: 369-374.
  16. Silverstein R, Bassler G, and Morrill T: Spectrometric identification of organic compounds, 5th ed. John Wiley & Sons, INC, New York (1991).
  17. El-Abd MAEH, El-Sheikh HH, Desouky S, Shehab A: Identification, Biodegradation and bio-evaluation of biopolymer produced from Bacillus thuringenesis. J Appl Pharm Sci. 2017; 7 (04): 103–110
  18. Gorenflo V, Steinbu¨chel A, and Marose S: Quantification of bacterial polyhydroxy-alkanoic acids by Nile red staining. Appl Microbiol Biotechnol 1999; 51:765–772
  19. El-Sheekh MM, El-Abd MA, El-Diwany AI: Poly-3 hydroxy butyrate production by Bacillus flexus ME-77 using some industrial wastes. Rend. Fis. Acc. Lincei 2015; 26(2):109–119.
  20. Desouky SE, El-Shiek HH, Elabd MA, and Shehab AM: Screening, optimization and extraction of polyhydroxyalkanoates from Bacillus thuringienesis. J. Adv. Biol. Biotechnol 2014; 1(1): 40–54.
  21. Kalaivani R, and Sukumaran V: Enhancement of technique for optimized production of PHA from marine bacteria, utilizing cheaply available carbon sources at Thanjavur district, India Int.J. Curr. Microbiol. App. Sci 2015; 4(4): 408–417.
  22. Naumann D, Helm D, Labischinski H: Microbiological characterization by FTIR spectroscopy. Nature 1991; 351:81–82.
  23. Medjeber N, Abbouni B, Menasria T, Beddal A, and Cherif N: Screening and production of polyhydroxyalcanoates by Bacillus megaterium by the using cane and beet molasses as carbon sources, Der Pharmacia Lettre 2015; 7 (6):102–109.
  24. Naheed N, and Jamil N: Optimization of biodegradable plastic production on sugar cane molasses in Enterobacter sp. SEL2. Braz. J. Microbiol 2014; 45(2):417–426.
  25. Sharma P, and Bajaj BK: Cost-effective substrates for production of-polyβ -hydroxybutrate by a newly isolated Bacillus cereus PS-10, J. Environ, Biol 2015; 36:1297–1304.
  26. Gouda M, Swellam A, and Omar S: Production of PHB by a Bacillus megaterium strain using sugarcane molasses and corn steep liquor as sole carbon and nitrogen source. Microbiol Res 2001; 156(3):201–207
  27. Lee WH, Loo CY, Nomura CT, Sudesh K: Biosynthesis of polyhydroxyalkanoate copolymers from mixtures of plant oils and 3- hydroxyvalerate precursors. Bioresour Technol 2008; 99 (15):6844–6851.
  28. Belal BE: Production of Poly-β -Hydroxybutyric Acid by Rhizobium elti and Pseudomonas stutzeri, Curr. Res. J. Biol. Sci 2013;5(6): 273–284.
  29. Tripathi AD, Yadav A, and Jha A, et al: Utilizing of sugar refinery waste (Cane Molasses) for production of bio-plastic under submerged fermentation process, J. Polym. Environ 2012; 20:446–453
  30. Ramadas NV, Singh SK, Socool CR: and Pande A. Polyhydroxylbutrate production using agro-industerial residue as substrate by Bacillus sphaericus NCIM 5149. Braz.Arch. Biol. Technol 2009; 52(1):17–23.
  31. Ryu HW, Hahn SK, Chang YK, and Chang HN: Production of poly3- hydroxybutyrate by high cell density fed batch culture of Alcaligenese utrophus with phosphate limitation. Biotechnol Bioengin 1997; 55(1): 27–
  32. Gomaa EZ: Production of polyhydroxyalkanoates by Bacillus subtilis and Escherichia coli grown on cane molasses fortified with ethanol, Braz. Arch. Biol. Technol 2014; 57 (1):145–154.
  33. Qiu YZ, Han J, Guo JJ, and Chen GQ: Production of poly (3- hydroxybutyrateco- 3-hydroxyhexanoate) from gluconate and glucose by recombinant Aeromonas hydrophila and Pseudomonas putida. Biotechnol Lett 2005; 27(18): 1381–1386.
  34. Sangkharak K, and Prasertsan P: Nutrient optimization for production of polyhydroxybutyrate from halotolerant photosynthetic bacteria cultivated under aerobic-dark condition Elect. J. Biotechnol 2008; 11 (3): 1–12.
  35. Sasidharan RS, Bhat SG, and Chandrasekaran M: Biocompatible polyhydroxybutyrate production by marine Vibrio azureus BTKB33 under submerged fermentation. Ann Microbiol 2015; 65 (1):455–465.
  36. Serafim LS, Lemos PC, Albuquerque MGE, and Reis MAM: Strategies for PHA production by mixed cultures and renewable waste materials, Appl. Microbiol. Biotechnol 2008; 81(4): 615–628.
  37. Reddy MV, Mawatari Y, Yajima Y, Satoh K, Mohan SV, Chang YC: Production of poly-3-hydroxybutyrate (P3HB) and poly(3- hydroxybutyrate-co-3-hydroxyvalerate) P(3HB-co-3HV) from synthetic wastewater using Hydrogenophaga palleronii. Bioresour. Technol 2016; 215: 155–162.
  38. Kemavongse K, Prasertsan P, Upaichit A, and Methacanon P: Effect of co-substrate on production of poly-β -hydroxybutyrate and copolymer PHBV from newly identified mutant Rhodobacter sphaeroides U7 cultivated under aerobic-dark condition Songklanakarin J. Sci. Technol 2007; 29(4): 1101–1113
  39. Hamieh A, Olama Z, and Holail H: Microbial production of polyhydroxybutyrate, a biodegradable plastic using agro-industrial waste products, Global Adv. Res. J. Microbiol 2013; 2(3): 054–064.
  40. Van-Thuoc D, Huu-Phong T, and Minh-Khuong D: A fed-batch fermentation process for poly (3-hydroxybutyrate-co-3-hydroxyvalerate) production by Yangia sp. Nd199 using molasses as substrate, TAP CHI SINH HOC 2015; 37(3): 325–331
  41. Dekwer D, and Hempel DC: Microaerophilic production of alginate by Azotobactervinelandii,Von der Gemeinsamen Naturwissenschaftlichen, Fakultat der Technischen UN. Carolo-Wilhelmina zuBraunschweig, Edited by Wael Sabra, aus Alexandria, Agypten 1999; 37–54.
  42. Dubois M, Gills KA, Hailton JK, Reberes PA, and Smit F: Colorimetric method for determination of sugar and related substances, Anal. Chem 1956; 28(3): 350–356.