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Article

Finding of Novel Galactose Utilizing Halomonas sp. YK44 for Polyhydroxybutyrate (PHB) Production

1
Department of Biological Engineering, College of Engineering, Konkuk University, Seoul 05029, Republic of Korea
2
Institute for Ubiquitous Information Technology and Applications, Konkuk University, Seoul 05029, Republic of Korea
3
Department of Biological and Chemical Engineering, Hongik University, Sejong 30016, Republic of Korea
4
Green & Sustainable Materials R&D Department, Research Institute of Clean Manufacturing System, Korea Institute of Industrial Technology (KITECH), Cheonan 31056, Republic of Korea
*
Author to whom correspondence should be addressed.
Polymers 2022, 14(24), 5407; https://doi.org/10.3390/polym14245407
Submission received: 3 November 2022 / Revised: 26 November 2022 / Accepted: 8 December 2022 / Published: 10 December 2022

Abstract

:
Polyhydroxybutyrate (PHB) is a biodegradable bioplastic with potential applications as an alternative to petroleum-based plastics. However, efficient PHB production remains difficult. The main cost of PHB production is attributed to carbon sources; hence, finding inexpensive sources is important. Galactose is a possible substrate for polyhydroxyalkanoate production as it is abundant in marine environments. Marine bacteria that produce PHB from galactose could be an effective resource that can be used for efficient PHB production. In this study, to identify a galactose utilizing PHB producer, we examined 16 Halomonas strains. We demonstrated that Halomonas cerina (Halomonas sp. YK44) has the highest growth and PHB production using a culture media containing 2% galactose, final 4% NaCl, and 0.1% yeast extract. These culture conditions yielded 8.98 g/L PHB (78.1% PHB content (w/w)). When galactose-containing red algae (Eucheuma spinosum) hydrolysates were used as a carbon source, 5.2 g/L PHB was produced with 1.425% galactose after treatment with activated carbon. Since high salt conditions can be used to avoid sterilization, we examined whether Halomonas sp. YK44 could produce PHB in non-sterilized conditions. Culture media in these conditions yielded 72.41% PHB content. Thus, Halomonas sp. YK44 is robust against contamination, allowing for long-term culture and economical PHB production.

1. Introduction

Plastic products are convenient in various fields such as food packaging, sterile medical uses, and construction. However, widespread plastic use leads to a huge amount of waste, which adversely affects the environment and humanity worldwide [1,2,3]. In particular, petroleum-based, non-degradable plastics cause environmental pollution, thus demonstrating the need for degradable plastic alternatives [4,5].
Polyhydroxyalkanoates (PHAs) are bioplastics that are potential alternatives to artificially synthesized plastics [6]. PHAs can be used for multiple applications such as biomedical devices, packaging, and coating materials. Poly(3-hydroxybutyrate) (PHB) is a PHA with properties similar to synthetic polymers [7]. PHB is produced by many microorganisms (Halomonas sp., Ralstonia eutropha, Bacillus sp., and Pseudomonas sp., etc.) [8,9], and several PHAs are produced by bacteria using commercial sugars [10,11]. PHB has a higher production cost than petrochemical plastics; hence, several researchers are studying low-cost PHA production by investigating readily available alternative and inexpensive carbon sources [12,13,14].
Marine biomasses such as large green algae, red algae, and brown macroalgae are promising because they present fast growth, large growth areas, and have low land, fertilizer, and water requirements [15]. In addition, these algae contain a large number of polysaccharides; hence, abundant monosaccharides can be derived from these species [16,17]. Among these, Eucheuma spinosum, red algae, grows in Southeast area and is used to produce agar and carrageenan [18]. Agar is a viscous complex polysaccharide constituting the cell wall of red algae and is a galactose polymer. Carrageenan is a linear polysaccharide composed of galactan with connected galactose residues [19]; 3,6-anhydrogalactose and sulfate ester groups are connected to the galactose unit, which cause structural deformation during acid treatment or heat treatment [20]. The ratio of 3,6-anhydrogalactose in E. spinosum is 56.2% galactose and 43.8% 3,6-anhydrogalactose [21,22,23,24].
The marine environment contains several strains that use galactose, suggesting that these could be used to generate galactose for PHB production [25,26,27,28]. Halomonas strains are present in salt-rich environments such as salt lakes, salt sand, salt soil, saline wells, solar salterns, saline wetlands, and marine environments [29,30]. Halomonas spp. can survive under high salinity [31,32], and their PHB production utilizing galactose has been organized into a table for comparison (Table 1) [25,26,27,28].
Many researchers examined PHB production using galactose in many marine strains (Table 1) [25,26,27,28], however, previous strains did not give significant titer for PHB production. As a result we tried to find out PHB producers with higher production capabilities from galactose and hypothesized that halotolerant bacteria could be applied to seaweed hydrolysates that have high salinity.
To realize this in this study, we identified Halomonas sp. YK44 as a potential PHB-producing species through utilizing galactose. Then, we examined the optimal culture media conditions for Halomonas sp. YK44 and tested its viability during PHB production. In addition, the E.spinosum hydrolysates were used to see if Halomonas could produce PHB using red algae that is abundant in marine environments [18].

2. Materials and Methods

2.1. Chemical Reagents

All chemicals used for cell culture were purchased from BD Difco Laboratories (Becton-Dickinson Franklin Lakes, NJ, USA). Reagents used for GC (Gas chromatography) and HPLC (High Performance Liquid Chromatography) analysis (chloroform, methanol, and other derivatization reagents) were purchased from Sigma-Aldrich (St. Louis, MO, USA). Red seaweed hydrolysate was prepared from E. spinosum, which was procured from the Korea Institute of Industrial Technology (Cheonan, KITECH, Korea). The lysate was prepared using dilute H2SO4 and an acid catalyst.

2.2. Sample Collection, Strain Isolation, and Phylogenetic Analysis

All sixteen strains were obtained from the National Marine Biodiversity Institute of Korea (Seochun, NMBIK, Korea). Each stock sample was suspended with distilled water and was spread on marine agar (MA; Difco Laboratories, Detroit, MI, USA) for isolation. The plates were incubated for two days at 30 °C. Colonies were isolated from each plate and cultured for one day in marine broth (MB; Difco Laboratories, Detroit, MI, USA). Stocks were prepared with 20% (w/v) glycerol and were stored at −81 °C until use.
The strain was identified at the species level using 16S rRNA. 16s rRNA was acquired from NMBIK, compared to those in the GenBank database of the NCBI using BLASTN tools, and used for making a phylogenetic tree utilizing MEGA 11 software, Molecular Evolutionary Genetics Analysis version 11 (Tamura, Stecher, and Kumar 2021).

2.3. Plate Assay for Strain Characterization

Plate assays were used to test the characteristics of the isolated strains [33]. An antibiotic susceptibility test was also performed via plate assay. The isolated strains were cultured for 2 days on MA with each antibiotic (100 µg/mL ampicillin, 25 µg/mL gentamicin, 50 µg/mL kanamycin, 100 µg/mL spectinomycin, and 25 µg/mL chloramphenicol). Colonies present after selection were considered resistant to the antibiotic.

2.4. Culture Conditions for PHA Synthesis

To identify which of the 16 Halomonas strains produces PHB, we cultivated 16 strains using MB containing 2% fructose. To optimize PHB production, Halomonas sp. YK44 was cultivated in the presence of various carbon and nitrogen sources. To determine which carbon source Halomonas uses, we added 2% glucose, xylose, galactose, glycerol, sucrose, fructose, or lactose to MB. Then, 0.1% yeast extract, NH4NO3, NH4CL, (NH4)HSO4, NH4NO3, and (NH4)2SO4 were used to determine the optimal nitrogen source. In addition, galactose (1–5% w/v) and yeast extract (0.1–1% w/v) were added to MB to optimize galactose and yeast extract concentrations. All experiments were performed in a shaking incubator at 30 °C (200 rpm) for 48 h. To determine optimal growth conditions, Halomonas sp. YK44 was cultured in MB with different concentrations of final NaCl (2–10% w/v) with 2% galactose and cultivated at 16 °C, 20 °C, 25 °C, 30 °C, 37 °C, and 42 °C. To confirm the optimal cultivation time for PHA production, Halomonas sp. YK44 was cultured in MB containing 2% galactose, final 4% NaCl, and 0.1% yeast extract at 25 °C for 96 h. The residual carbon source concentration was evaluated by HPLC using a PerkinElmer system equipped with a refractive index detector (Waltham, MA, USA) and an Aminex HPX-87H column (300 × 7.8 mm internal diameter)(Dublin, Ireland). The flow rate of the mobile phase containing 0.008 N sulfuric acid was constantly maintained at 0.6 mL/min. The oven temperature was set at 60 °C [34].

2.5. Analytical Methods

Using GC, PHB were quantified and characterized as previously described [34,35]. After culturing, the broth was centrifuged to collect cell pellets, which were subsequently washed twice with deionized water. After adjusting the amount of water to match the culture volume, 1 mL samples were collected in a glass vial for lyophilization. The dry weight of the lyophilized pellet was measured. Then, 1 mL chloroform and 1 mL 15% (v/v) H2SO4/85% methanol solution were added to the dried cell pellet. Methanolysis was conducted while heating for 2 h at 100 °C. After cooling to room temperature (25 °C), 1 mL of deionized water was added to the methyl ester solution, which was vortexed for approximately 5 s. The chloroform layer was carefully extracted and transferred to a microtube containing sodium sulfate anhydrous to remove any remaining water. Samples were filtered through a 0.22-μm Millex-GP syringe filter unit and 1 μL aliquots were injected into a gas chromatograph with split mode (1/10) (Young-lin 6500, Seoul, Korea), equipped with a fused silica capillary column (Agilent HP-FFAP, 30 m × 0.32 mm, i.d. 0.25 μm film) and a flame ionization detector (FID). The inlet temperature was 210 °C and helium carrier gas was supplied at 3 mL/min. The oven temperature was controlled following a gradient program of 0–5 min at 80 °C and 12–17 min at 220 °C. The FID temperature was maintained at 230 °C throughout the operation [34,36,37].

2.6. TEM Analysis

To conduct TEM analysis, 1 mL of cultured sample was collected, centrifuged, and mixed with Karnovsky’s fixative solution containing 2% glutaraldehyde. The sample was fixed with 1% osmium tetroxide in 0.05 M sodium cacodylate buffer. The cells were gradually dehydrated using an ascending ethanol gradient (50%, 70%, 95%, and 100% v/v). Propylene was used for the transition step. The sample was settled in different ratios of propylene oxide and Spurr’s resin (v/v) (1:1 and 1:2). After mixing with 100% Spurr’s resin, the sample solidified overnight at 70 °C in a dry oven. Then, the samples were cut with an ultramicrotome (LEICA, EM UC7, Wetzlar, Germany). The slices were placed on a grid for EF-TEM (Carl Zeiss, LIBRA 120, Oberkochen, Germany) with an accelerating voltage of 120 kV [34].

2.7. Polymer Extraction and Characterization

Halomonas sp. YK44 cells were cultivated in 40 mL MB medium with 2% galactose for 48 h at 25 °C. The cells were pelleted, washed twice with deionized water, and lyophilized. Approximately 20 mL chloroform was added to the lyophilized cells and PHB was extracted for 16 h at 60 °C. The chloroform layer with dissolved polymer was collected by centrifugation and filtered using Whatman No. 1 filter paper to remove cell debris. The chloroform was evaporated at room temperature, to make a PHB film. The film was analyzed by differential scanning calorimetry (DSC) and gel permeation chromatography (GPC) [35,38].
DSC was used to analyze the extracted PHB film. Analysis was conducted with a Discovery DSC instrument (TA Instrument, Delaware, USA) from −60 °C to 180 °C. The heating and cooling rate was 10 °C/min in an N2 atmosphere. PHB powder (Sigma-Aldrich) was used as a standard.
GPC analysis was performed using a GPC instrument (YL Chromass, Anyang, Korea) with a loop injector (Rheodyne 7725i), dual-head isocratic pump (YL9112), column oven (YL9131), column (Shodex, K-805, 8.0 I.D. × 300 mm), and RI detector (YL9170). For GPC analysis, 0.1 g PHB film was dissolved in chloroform and passed through a 0.2-μm syringe filter (Chromdisc, Hwaseong, Korea). Here, 60 μL of this solution (without air bubbles) was used as the injection volume. The flow rate of the chloroform mobile phase was 1 mL/min and was maintained at 35 °C. The molecular masses of 5000–2,000,000 Da were compared to polystyrene standards using YL-Clarity software (YL Chromass, Anyang, Korea).

2.8. PHB Production in E. spinosum Hydrolysate

Halomonas sp. YK44 was cultured with E. spinosum hydrolysate in MB. To determine the optimal culture growth conditions, Halomonas sp. YK44 was cultured in MB with different concentrations of E. spinosum hydrolysate (final galactose concentration: 0.475–1.9% w/v) and pH 6–10. DCW and PHB were measured after 2 days of cultivation at 30 °C while shaking at 200 rpm. The salinity of E. spinosum hydrolysate was analyzed using a digital salinity tester (ATAGO, Tokyo, Japan).
The E. spinosum hydrolysate was treated with 1 g/L activated carbon. Activated carbon treatment was performed by shaking for 5 min and centrifuging at 3700 rpm for 15 min. The treated hydrolysate was filtered using a 0.2-μm syringe filter (Chromdisc, Hwaseong, Korea).

2.9. PHB Production Reusing Non-Sterilized and Sterilized Medium for Comparison

With or without sterilization, Halomonas sp. YK44 was cultured in a high salinity MB medium with final 6% NaCl, 2% galactose and 0.1% yeast extract for 2 days at 25 °C and 200 rpm for comparing non-sterilized and sterilized media.
Culture medium reuse experiments were conducted by comparing culture media in sterilized medium with that in non-sterilized media. After centrifugation, the supernatant was collected and reused. We added 2% galactose and 0.1% yeast extract to the reused culture medium each cycle. It was done 10 cycles in total.

3. Results

3.1. Isolation and Characterization of Marine Strains for PHA Production

16 Halomonas strains were cultured in MB containing 2% fructose and analyzed for PHB production using GC. Among them, we found that Halomonas sp. YK44 produces the highest amount of PHB (11.5 g/L of DCW, 6.8 g/L w/w PHB; 58.8% PHB content) (Table 2, Figure 1A). Strain YK44 showed high 16s rRNA sequence similarity (97.93%) with H. cerina SP4 (red box) (Figure 1B) according to phylogenetic analysis. Given the high PHB peak, Halomonas sp. YK44 was selected for further study.
Halomonas sp. YK44 was assessed for hydrolase activity, antibiotic resistance, carbon and nitrogen source utility, growth temperature, and salt resistance. Halomonas sp. YK44 did not show any hydrolase activity. To evaluate antibiotic resistance, the isolated strain was cultured in MB containing each 100 µg/mL ampicillin, 25 µg/mL gentamicin, 50 µg/mL kanamycin, 100 µg/mL spectinomycin, and 25 µg/mL chloramphenicol. Strain YK44 showed the highest resistance on the ampicillin plate. The strain was also resistant to spectinomycin (Supplementary Table S1). When YK44 was tested for poly(3-hydroxybutyrate-co-3-hydroxyvalerate) (P(3HB-co-3HV) production from propionate, it produced only 0.43% 3HV.
To visualize PHA accumulation in Halomonas sp. YK44, the strain was cultured for 48 h at 25 °C in MB with 2% galactose, final 4% NaCl, and 0.1% yeast extract. Then, TEM analysis was conducted. TEM showed PHB granule accumulation in the cells after 48 h cultivation (Figure 1C). The PHB granules completely filled the cytoplasm showing Halomonas sp. YK44 produces PHB.

3.2. Evaluating Carbon and Nitrogen Sources for PHB Production

Among the tested carbon sources (2% glucose, xylose, fructose, galactose, sucrose, glycerol), Halomonas sp. YK44 showed the best growth with sucrose but showed higher PHB production in the presence of galactose (Figure 2A; Table 1). To optimize the galactose concentration, we compared PHB production with different galactose concentrations (1–5% w/v). Growth and PHB production were the highest at 2% galactose; hence, this percentage was used for further analysis (Figure 2B).
Multiple nitrogen sources, such as 0.1% yeast extract, NH4NO3, NH4CL, (NH4)HSO4, NH4NO3, and (NH4)2SO4, were added to MB to determine the optimal nitrogen source. Halomonas sp. YK44 showed the most growth and PHB production with 0.1% yeast extract, followed by (NH4)2SO4 (Figure 2C). To optimize the concentration of yeast extract, we compared PHB production in MB with different yeast extract concentrations (0.1–1% w/v). However, additional yeast extract did not change PHB production. Since PHB production was similar in MB containing 0.1% and 1% yeast extract, we decided to use 0.1% yeast extract to facilitate economical PHB production (Figure 2D).

3.3. Examination of Culture Temperature, Time, and NaCl Concentration

To determine the optimum culture conditions, we first examined different culture temperatures. When cultured at 16, 20, 25, 30, 37, and 42 °C, YK44 showed the best growth and PHB production at 25 °C (Figure 3A). Other studies mainly cultured Halomonas strains at 30 °C and 37 °C [39,40,41]. YK44 can grow and produce PHB at 25 °C similar to room temperature.
Since Halomonas sp. YK44 is halotolerant and can grow under high NaCl conditions, we examined how various salt concentrations affected PHB production (Figure 3B). Growth and PHB production were highest under final 4% NaCl, though there was no difference of more than 2 g/L from 2% to final 8% NaCl.
To determine the optimal Halomonas sp. YK44 culture time, growth in the optimized medium was monitored every 24 h for 4 days. The highest growth and PHB production were observed after 48 h (Figure 3C), with PHB production reaching 8.98 g/L PHB (75.11% PHB content w/w) and 11.6 g/L DCW. Culturing for more than 48 h did not increase PHB production, likely because most of the sugar was consumed. Finally, 20 g/L of galactose was completely consumed after 72 h.

3.4. Chemical Properties and Molecular Weight of PHB from Halomonas sp. YK44

PHB film was extracted from 40 mL of optimized cultivation media after 48 h cultivation at optimal culture conditions (25 °C in MB containing 2% galactose, final 4% NaCl, and 0.1% yeast extract) (Supplementary Figure S2). The melting and crystallization temperatures of the extracted PHB film were Tm = 170.57 °C and Tc = 126.60 °C, respectively. These values were similar to those of authentic PHB film: Tm = 176.55 °C and Tc = 126.29 °C (Supplementary Figure S1). Further, the Tm and Tc values were similar to those of authentic films and PHB films derived from other PHB producer strains [42,43,44].
To characterize the number average molecular weight (Mw), the weight average molecular weight (Mn), and the polydispersity index (PDI = Mw/Mn) of PHB extracted from Halomonas sp. YK44, we performed a GPC analysis. The Mw, Mn, and PDI of extracted PHB were 7.92 × 105, 6.90 × 105, and 1.48, respectively. GPC analysis revealed that strain YK44 produced higher molecular weight polymers than authentic PHB films (Mw = 4.29 × 105, Mn = 3.19 × 105, PDI = 1.34) (Supplementary Table S2). A high molecular weight polymer indicates high PHB quality, which is advantageous for industrial applications. Reduced molar masses during extraction are likely caused by damage to the granules. Compared with authentic PHB, intracellular PHB has low polydispersity; PDI is narrower than authentic PHB film. The narrow dispersity means homogeneous polymers [45,46].

3.5. PHB Production using E. spinosum Hydrolysates

To determine possible applications of Halomonas sp. YK44, cells were cultured in MB containing E. spinosum hydrolysate. The salinity of E. spinosum hydrolysates was approximately 2.6% and contained 3.8% galactose. To optimize the pH of E. spinosum hydrolysate, we compared PHB production capacity in the MB medium at different pH values. Growth and PHB production were the highest at pH 10 (Figure 4A). Further, growth was suppressed at galactose concentrations higher than 0.95%, possibly due to the influence of inhibitors. The highest cell growth and PHB production were obtained with 0.95% galactose concentration from E. spinosum hydrolysate in MB. Culturing in these conditions returned 4.9 g/L DCW and 27.2% PHB content (Figure 4B).
Activated carbon was used to remove impurities from the hydrolysate as activated carbon treatment removes toxic substances that may be released during hydrolysis [47,48]. Halomonas sp. YK44 showed optimal growth with 0.95% galactose but activated carbon treatment led to growth in media containing 1.9% galactose. Moreover, 5.2 g/L PHB was produced under 1.425% galactose culture condition (Figure 4C), which was 3.92-fold higher than the culture without activated carbon. These results suggest that activated carbon treatment increases hydrolysate utilization.

3.6. PHB Production in Reusing High Saline Non-Sterilized Medium and Sterilized Medium

To examine possible applications of Halomonas sp. YK44, we investigated whether this strain could be cultured in non-sterilized high-salt media without contamination and whether these culture conditions would change PHB production [49,50]. In sterilized or non-sterilized MB with final 6% NaCl and 2% galactose, Halomonas sp. YK44 produced PHB with or without sterilization. In non-sterilized samples, the highest amount of PHB was 7.24 g/L from 10.00 g/L DCW (72.41% PHB content w/w) in non-sterilized samples. This was comparable with results for sterilized media, which yielded 7.13 g/L PHB from 9.50 g/L DCW (75.02% PHB content w/w) (Figure 5). Overall, these results indicate that Halomonas sp. YK44 produces PHB under non-sterilized conditions like sterilized conditions.
When comparing sterilized and non-sterile media for reperirive use of media, there is no significant difference in growth or PHB production, indicating that Halomonas sp. YK44 could be cultured in non-sterilized medium without contamination. Accumulated data over 10 cycles indicated that PHB production showed a difference of approximately 1.8 g/L, but this difference was not significant considering that it is an accumulation of PHB production (Figure 5). Thus, Halomonas sp. YK44 shows high robustness to contamination, which will facilitate PHB production for industrial applications.

4. Discussion

As Halomonas spp. can usually survive and produce PHB at high salinity, it is possible to utilize open non-sterile fermentation in a high salinity medium without antibiotics treatment or sterilization [31,32]. In addition, as this Halomonas strain is a benign native PHB producer, it is free of any environmental issues such as the law of genetically modified objects or pathogen issues. Since Halomonas sp. YK44 is salt-tolerant and uses galactose, this strain can be used to produce PHB by utilizing seaweed hydrolysate like Euchenoma spinosum hydrolysate resulting in reduced PHB production cost. Our results suggest that not only can red algae be used to produce PHB, but also that it allows microorganisms to grow better when hydrolysates are treated with activated carbon, as shown in other papers [51,52].
In conclusion, we determined that Halomonas sp. YK44 strain produces more PHB using galactose as a carbon source among 16 Halomonas strains. According to Figure 3B, as Halomonas sp. YK44 is salt-tolerant and uses galactose, it can be used to produce PHB utilizing seaweed hydrolysate. PHB was produced using E. spinosum hydrolysates that have abundant galactose with a salinity of 2.6% and production increased after activated carbon treatment. Furthermore, we reused the media to compare PHB productivity with sterilized and non-sterilized high-salt media to determine that Halomonas is resistant to contamination in high salinity conditions. Total PHB production showed no significant difference between cultures in sterilized or non-sterilized high-salinity culture media. Thus, cost-effective application will be possible even if PHB is produced using by-products without sterilization.
In Halomonas sp. YK44, PHB was effectively produced using various sugar components, especially galactose. We optimized culture media conditions to produce PHB in MB media with 2% galactose, 0.1% yeast extract, and final 4% NaCl concentration under 25 °C for 48 h. Under optimized PHB production conditions, the strain produced 8.98 g/L PHB from 11.6 g/L DCW (78.11% PHB content). Halomonas sp. YK44 showed about 50% more production than the maximum amount of the previously reported paper [25,26,27,28]. Similar PHB content was produced in MB medium containing final 2–8% NaCl. This suggests that Halomonas sp. YK44 is salt-tolerant similar to other Halomonas spp. [53,54]. Since PHB was produced at a low temperature (25 °C), it may be possible to produce only by shaking at room temperature. For PHB production and cultivation using E. spinosum hydrolysate, 1.425 g/L galactose, and activated carbon, the yield was 5.2 g/L PHB, which was the largest amount we produced using E. spinosum hydrolysates. In MB media with final 6% NaCl and 2% galactose without antibiotics and sterilization, PHB production was 4.2 g/L PHB from 7.3 g/L DCW.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/polym14245407/s1, Figure S1: DSC analysis of PHB from Halomonas sp. YK44; Table S1: Species identification using 16S rRNA sequencing and antibiotic resistance the identified strain.; Figure S2: GPC analysis of PHB from Halomonas sp. YK44; Table S2: Comparison of GPC analysis result Halomonas sp. YK44 film and Authentic PHB film; Figure S2; PHB film extracted from Halomonas sp. YK44.

Author Contributions

Conceptualization, H.J.J., S.K.B. and Y.-H.Y.; methodology, H.J.J., S.K.B. and Y.-H.Y.; validation, S.H.K., D.H.C. and B.C.K.; resources, J.-M.J. and J.-J.Y.; writing—original draft preparation, H.J.J.; writing—review and editing, S.K.B., J.L. and Y.-H.Y.; supervision, Y.-H.Y.; project administration, S.K.B. and Y.-H.Y. All authors have read and agreed to the published version of the manuscript.

Funding

This research was supported by Research Program to solve social issues of the National Research Foundation of Korea (NRF)s funded by the Ministry of Science and ICT, South Korea [grant number 2017M3A9E4077234] and [NRF-2022R1A2C2003138, NRF-2020R1A2C2102381]. This study was also performed with the support of the R&D Program for Forest Science Technology [grant number 2020261C10-2222-AC02] provided by Korea Forest Service (Korea Forestry Promotion Institute) and by the R&D Program of MOTIE/KEIT (20018072).

Institutional Review Board Statement

Not applicable.

Data Availability Statement

All data related to the study are provided with the manuscript and its associated files.

Conflicts of Interest

The authors declare that they have no known competing financial interest or personal relationships that could have influenced the work reported in this paper.

References

  1. Barnes, D.K.A.; Galgani, F.; Thompson, R.C.; Barlaz, M. Accumulation and Fragmentation of Plastic Debris in Global Environments. Philos. Trans. R. Soc. B Biol. Sci. 2009, 364, 1985–1998. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  2. Chamas, A.; Moon, H.; Zheng, J.; Qiu, Y.; Tabassum, T.; Jang, J.H.; Abu-Omar, M.; Scott, S.L.; Suh, S. Degradation Rates of Plastics in the Environment. ACS Sustain. Chem. Eng. 2020, 8, 3494–3511. [Google Scholar] [CrossRef] [Green Version]
  3. Patrício Silva, A.L.; Prata, J.C.; Walker, T.R.; Duarte, A.C.; Ouyang, W.; Barcelò, D.; Rocha-Santos, T. Increased Plastic Pollution Due to COVID-19 Pandemic: Challenges and Recommendations. Chem. Eng. J. 2021, 405, 126683. [Google Scholar] [CrossRef] [PubMed]
  4. Vieira, M.G.A.; da Silva, M.A.; dos Santos, L.O.; Beppu, M.M. Natural-Based Plasticizers and Biopolymer Films: A Review. Eur. Polym. J. 2011, 47, 254–263. [Google Scholar] [CrossRef] [Green Version]
  5. Kabir, E.; Kaur, R.; Lee, J.; Kim, K.H.; Kwon, E.E. Prospects of Biopolymer Technology as an Alternative Option for Non-Degradable Plastics and Sustainable Management of Plastic Wastes. J. Clean. Prod. 2020, 258, 120536. [Google Scholar] [CrossRef]
  6. Costa, S.S.; Miranda, A.L.; de Morais, M.G.; Costa, J.A.V.; Druzian, J.I. Microalgae as Source of Polyhydroxyalkanoates (PHAs)—A Review. Int. J. Biol. Macromol. 2019, 131, 536–547. [Google Scholar] [CrossRef]
  7. Khosravi-Darani, K.; Mokhtari, Z.B.; Amai, T.; Tanaka, K. Microbial Production of Poly(Hydroxybutyrate) from C1 Carbon Sources. Appl. Microbiol. Biotechnol. 2013, 97, 1407–1424. [Google Scholar] [CrossRef]
  8. Venkateswar Reddy, M.; Mawatari, Y.; Yajima, Y.; Seki, C.; Hoshino, T.; Chang, Y.C. Poly-3-Hydroxybutyrate (PHB) Production from Alkylphenols, Mono and Poly-Aromatic Hydrocarbons Using Bacillus sp. CYR1: A New Strategy for Wealth from Waste. Bioresour. Technol. 2015, 192, 711–717. [Google Scholar] [CrossRef] [Green Version]
  9. Tsuge, T.; Hyakutake, M.; Mizuno, K. Class IV Polyhydroxyalkanoate (PHA) Synthases and PHA-Producing Bacillus. Appl. Microbiol. Biotechnol. 2015, 99, 6231–6240. [Google Scholar] [CrossRef]
  10. Hempel, F.; Bozarth, A.S.; Lindenkamp, N.; Klingl, A.; Zauner, S.; Linne, U.; Steinbüchel, A.; Maier, U.G. Microalgae as Bioreactors for Bioplastic Production. Microb. Cell Factories 2011, 10, 81. [Google Scholar] [CrossRef]
  11. Verlinden, R.A.J.; Hill, D.J.; Kenward, M.A.; Williams, C.D.; Radecka, I. Bacterial Synthesis of Biodegradable Polyhydroxyalkanoates. J. Appl. Microbiol. 2007, 102, 1437–1449. [Google Scholar] [CrossRef] [PubMed]
  12. Cui, Y.W.; Zhang, H.Y.; Lu, P.F.; Peng, Y.Z. Effects of Carbon Sources on the Enrichment of Halophilic Polyhydroxyalkanoate-Storing Mixed Microbial Culture in an Aerobic Dynamic Feeding Process. Sci. Rep. 2016, 6, 30766. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  13. Getachew, A.; Woldesenbet, F. Production of Biodegradable Plastic by Polyhydroxybutyrate (PHB) Accumulating Bacteria Using Low Cost Agricultural Waste Material. BMC Res. Notes 2016, 9, 509. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  14. Saratale, R.G.; Saratale, G.D.; Cho, S.K.; Kim, D.S.; Ghodake, G.S.; Kadam, A.; Kumar, G.; Bharagava, R.N.; Banu, R.; Shin, H.S. Pretreatment of Kenaf (Hibiscus cannabinus L.) Biomass Feedstock for Polyhydroxybutyrate (PHB) Production and Characterization. Bioresour. Technol. 2019, 282, 75–80. [Google Scholar] [CrossRef]
  15. Sawant, S.S.; Salunke, B.K.; Kim, B.S. Consolidated Bioprocessing for Production of Polyhydroxyalkanotes from Red Algae Gelidium amansii. Int. J. Biol. Macromol. 2018, 109, 1012–1018. [Google Scholar] [CrossRef]
  16. Jung, K.A.; Lim, S.R.; Kim, Y.; Park, J.M. Potentials of Macroalgae as Feedstocks for Biorefinery. Bioresour. Technol. 2013, 135, 182–190. [Google Scholar] [CrossRef]
  17. Wei, N.; Quarterman, J.; Jin, Y.S. Marine Macroalgae: An Untapped Resource for Producing Fuels and Chemicals. Trends Biotechnol. 2013, 31, 70–77. [Google Scholar] [CrossRef]
  18. Rhein-Knudsen, N.; Ale, M.T.; Meyer, A.S. Marine Drugs Seaweed Hydrocolloid Production: An Update on Enzyme Assisted Extraction and Modification Technologies. Mar. Drugs 2015, 13, 3340–3359. [Google Scholar] [CrossRef]
  19. Estevez, J.M.; Ciancia, M.; Cerezo, A.S. The System of Sulfated Galactans from the Red Seaweed Gymnogongrus torulosus (Phyllophoraceae, Rhodophyta): Location and Structural Analysis. Carbohydr. Polym. 2008, 73, 594–605. [Google Scholar] [CrossRef]
  20. Campo, V.L.; Kawano, D.F.; da Silva, D.B.; Carvalho, I. Carrageenans: Biological Properties, Chemical Modifications and Structural Analysis—A Review. Carbohydr. Polym. 2009, 77, 167–180. [Google Scholar] [CrossRef]
  21. Kim, M.-J.; Kim, J.-S.; Ra, C.H.; Kim, S.-K. Bioethanol Production from Eucheuma spinosum Using Various Yeasts. KSBB J. 2013, 28, 315–318. [Google Scholar] [CrossRef] [Green Version]
  22. Ra, C.H.; Jung, J.H.; Sunwoo, I.Y.; Kang, C.H.; Jeong, G.T.; Kim, S.K. Detoxification of Eucheuma Spinosum Hydrolysates with Activated Carbon for Ethanol Production by the Salt-Tolerant Yeast Candida tropicalis. J. Microbiol. Biotechnol. 2015, 25, 856–862. [Google Scholar] [CrossRef] [PubMed]
  23. Adnan, H.; Porse, H. Culture of Eucheuma cottonii and Eucheuma spinosum in Indonesia. Hydrobiologia 1987, 151–152, 355–358. [Google Scholar] [CrossRef]
  24. Andersen, N.S.; Dolan, T.C.S.; Rees, D.A. Carrageenans. Part VII. Polysaccharides from Eucheuma spinosum and Eucheuma cottonii. The Covalent Structure of L-Carrageenan. J. Chem. Soc. Perkin 1 1973, 19, 2173–2176. [Google Scholar] [CrossRef] [PubMed]
  25. Pernicova, I.; Kucera, D.; Novackova, I.; Vodicka, J.; Kovalcik, A.; Obruca, S. Extremophiles—Platform Strains for Sustainable Production of Polyhydroxyalkanoates. In Materials Science Forum; Trans Tech Publications Ltd.: Wollerau, Switzerland, 2019; Volume 955, pp. 74–79. [Google Scholar]
  26. Thirumala, M.; Reddy, S.V.; Mahmood, S.K. Production and Characterization of PHB from Two Novel Strains of Bacillus Spp. Isolated from Soil and Activated Sludge. J. Ind. Microbiol. Biotechnol. 2010, 37, 271–278. [Google Scholar] [CrossRef]
  27. Kucera, D.; Pernicová, I.; Kovalcik, A.; Koller, M.; Mullerova, L.; Sedlacek, P.; Mravec, F.; Nebesarova, J.; Kalina, M.; Marova, I.; et al. Characterization of the Promising Poly(3-Hydroxybutyrate) Producing Halophilic Bacterium Halomonas halophila. Bioresour. Technol. 2018, 256, 552–556. [Google Scholar] [CrossRef] [PubMed]
  28. Thomas, T.; Sudesh, K.; Bazire, A.; Elain, A.; Tan, H.T.; Lim, H.; Bruzaud, S. PHA Production and Pha Synthases of the Halophilic Bacterium Halomonas sp. SF2003. Bioengineering 2020, 7, 29. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  29. Poli, A.; Nicolaus, B.; Denizci, A.A.; Yavuzturk, B.; Kazan, D. Halomonas Smyrnensis sp. Nov., a Moderately Halophilic, Exopolysaccharide-Producing Bacterium. Int. J. Syst. Evol. Microbiol. 2013, 63, 10–18. [Google Scholar] [CrossRef]
  30. Xu, X.W.; Wu, Y.H.; Zhou, Z.; Wang, C.S.; Zhou, Y.G.; Zhang, H.B.; Wang, Y.; Wu, M. Halomonas saccharevitans sp. Nov., Halomonas arcis sp. Nov. and Halomonas subterranea sp. Nov., Halophilic Bacteria Isolated from Hypersaline Environments of China. Int. J. Syst. Evol. Microbiol. 2007, 57, 1619–1624. [Google Scholar] [CrossRef]
  31. Ling, C.; Qiao, G.Q.; Shuai, B.W.; Song, K.N.; Yao, W.X.; Jiang, X.R.; Chen, G.Q. Engineering Self-Flocculating Halomonas campaniensis for Wastewaterless Open and Continuous Fermentation. Biotechnol. Bioeng. 2019, 116, 805–815. [Google Scholar] [CrossRef]
  32. Fu, X.Z.; Tan, D.; Aibaidula, G.; Wu, Q.; Chen, J.C.; Chen, G.Q. Development of Halomonas TD01 as a Host for Open Production of Chemicals. Metab. Eng. 2014, 23, 78–91. [Google Scholar] [CrossRef] [PubMed]
  33. Lee, S.M.; Lee, H.J.; Kim, S.H.; Suh, M.J.; Cho, J.Y.; Ham, S.; Jeon, J.M.; Yoon, J.J.; Bhatia, S.K.; Gurav, R.; et al. Screening of the Strictly Xylose-Utilizing Bacillus sp. SM01 for Polyhydroxybutyrate and Its Co-Culture with Cupriavidus necator NCIMB 11599 for Enhanced Production of PHB. Int. J. Biol. Macromol. 2021, 181, 410–417. [Google Scholar] [CrossRef] [PubMed]
  34. Park, Y.L.; Bhatia, S.K.; Gurav, R.; Choi, T.R.; Kim, H.J.; Song, H.S.; Park, J.Y.; Han, Y.H.; Lee, S.M.; Park, S.L.; et al. Fructose Based Hyper Production of Poly-3-Hydroxybutyrate from Halomonas sp. YLGW01 and Impact of Carbon Sources on Bacteria Morphologies. Int. J. Biol. Macromol. 2020, 154, 929–936. [Google Scholar] [CrossRef] [PubMed]
  35. Jung, H.R.; Choi, T.R.; Han, Y.H.; Park, Y.L.; Park, J.Y.; Song, H.S.; Yang, S.Y.; Bhatia, S.K.; Gurav, R.; Park, H.A.; et al. Production of Blue-Colored Polyhydroxybutyrate (PHB) by One-Pot Production and Coextraction of Indigo and PHB from Recombinant Escherichia coli. Dye. Pigment. 2020, 173, 107889. [Google Scholar] [CrossRef]
  36. Hong, J.W.; Song, H.S.; Moon, Y.M.; Hong, Y.G.; Bhatia, S.K.; Jung, H.R.; Choi, T.R.; Yang, S.Y.; Park, H.Y.; Choi, Y.K.; et al. Polyhydroxybutyrate Production in Halophilic Marine Bacteria Vibrio Proteolyticus Isolated from the Korean Peninsula. Bioprocess. Biosyst. Eng. 2019, 42, 603–610. [Google Scholar] [CrossRef]
  37. Bhatia, S.K.; Gurav, R.; Choi, T.R.; Jung, H.R.; Yang, S.Y.; Moon, Y.M.; Song, H.S.; Jeon, J.M.; Choi, K.Y.; Yang, Y.H. Bioconversion of Plant Biomass Hydrolysate into Bioplastic (Polyhydroxyalkanoates) Using Ralstonia eutropha 5119. Bioresour. Technol. 2019, 271, 306–315. [Google Scholar] [CrossRef]
  38. Bhatia, S.K.; Wadhwa, P.; Hong, J.W.; Hong, Y.G.; Jeon, J.M.; Lee, E.S.; Yang, Y.H. Lipase Mediated Functionalization of Poly(3-Hydroxybutyrate-Co-3-Hydroxyvalerate) with Ascorbic Acid into an Antioxidant Active Biomaterial. Int. J. Biol. Macromol. 2019, 123, 117–123. [Google Scholar] [CrossRef]
  39. Tohme, S.; Hacıosmanoğlu, G.G.; Eroğlu, M.S.; Kasavi, C.; Genç, S.; Can, Z.S.; Toksoy Oner, E. Halomonas smyrnensis as a Cell Factory for Co-Production of PHB and Levan. Int. J. Biol. Macromol. 2018, 118, 1238–1246. [Google Scholar] [CrossRef]
  40. Kulkarni, S.O.; Kanekar, P.P.; Jog, J.P.; Sarnaik, S.S.; Nilegaonkar, S.S. Production of Copolymer, Poly (Hydroxybutyrate-Co-Hydroxyvalerate) by Halomonas campisalis MCM B-1027 Using Agro-Wastes. Int. J. Biol. Macromol. 2015, 72, 784–789. [Google Scholar] [CrossRef]
  41. Jiang, X.R.; Yao, Z.H.; Chen, G.Q. Controlling Cell Volume for Efficient PHB Production by Halomonas. Metab. Eng. 2017, 44, 30–37. [Google Scholar] [CrossRef]
  42. Trakunjae, C.; Boondaeng, A.; Apiwatanapiwat, W.; Kosugi, A.; Arai, T.; Sudesh, K.; Vaithanomsat, P. Enhanced Polyhydroxybutyrate (PHB) Production by Newly Isolated Rare Actinomycetes Rhodococcus sp. Strain BSRT1-1 Using Response Surface Methodology. Sci. Rep. 2021, 11, 1896. [Google Scholar] [CrossRef] [PubMed]
  43. Radhika, D.; Murugesan, A.G. Bioproduction, Statistical Optimization and Characterization of Microbial Plastic (Poly 3-Hydroxy Butyrate) Employing Various Hydrolysates of Water Hyacinth (Eichhornia crassipes) as Sole Carbon Source. Bioresour. Technol. 2012, 121, 83–92. [Google Scholar] [CrossRef]
  44. Wellen, R.M.R.; Rabello, M.S.; Fechine, G.J.M.; Canedo, E.L. The Melting Behaviour of Poly(3-Hydroxybutyrate) by DSC. Reproducibility Study. Polym. Test 2013, 32, 215–220. [Google Scholar] [CrossRef]
  45. Wendlandt, K.D.; Geyer, W.; Mirschel, G.; Al-Haj Hemidi, F. Possibilities for Controlling a PHB Accumulation Process Using Various Analytical Methods. J. Biotechnol. 2005, 117, 119–129. [Google Scholar] [CrossRef]
  46. Alsafadi, D.; Ibrahim, M.I.; Alamry, K.A.; Hussein, M.A.; Mansour, A. Utilizing the Crop Waste of Date Palm Fruit to Biosynthesize Polyhydroxyalkanoate Bioplastics with Favorable Properties. Sci. Total Environ. 2020, 737, 139716. [Google Scholar] [CrossRef]
  47. Arminda, M.; Josúe, C.; Cristina, D.; Fabiana, S.; Yolanda, M. Use of Activated Carbons for Detoxification of a Lignocellulosic Hydrolysate: Statistical Optimisation. J. Environ. Manag. 2021, 296, 113320. [Google Scholar] [CrossRef] [PubMed]
  48. Sahu, A.K.; Srivastava, V.C.; Mall, I.D.; Lataye, D.H. Adsorption of Furfural from Aqueous Solution onto Activated Carbon: Kinetic, Equilibrium and Thermodynamic Study. Sep. Sci. Technol. 2008, 43, 1239–1259. [Google Scholar] [CrossRef]
  49. Tan, D.; Xue, Y.S.; Aibaidula, G.; Chen, G.Q. Unsterile and Continuous Production of Polyhydroxybutyrate by Halomonas TD01. Bioresour. Technol. 2011, 102, 8130–8136. [Google Scholar] [CrossRef]
  50. Park, Y.L.; Song, H.S.; Choi, T.R.; Lee, S.M.; Park, S.L.; Lee, H.S.; Kim, H.J.; Bhatia, S.K.; Gurav, R.; Park, K.; et al. Revealing of Sugar Utilization Systems in Halomonas sp. YLGW01 and Application for Poly(3-Hydroxybutyrate) Production with Low-Cost Medium and Easy Recovery. Int. J. Biol. Macromol. 2021, 167, 151–159. [Google Scholar] [CrossRef]
  51. Parawira, W.; Tekere, M. Biotechnological Strategies to Overcome Inhibitors in Lignocellulose Hydrolysates for Ethanol Production: Review. Crit. Rev. Biotechnol. 2011, 31, 20–31. [Google Scholar] [CrossRef]
  52. Lee, J.M.; Venditti, R.A.; Jameel, H.; Kenealy, W.R. Detoxification of Woody Hydrolyzates with Activated Carbon for Bioconversion to Ethanol by the Thermophilic Anaerobic Bacterium Thermoanaerobacterium saccharolyticum. Biomass Bioenergy 2011, 35, 626–636. [Google Scholar] [CrossRef]
  53. El-malek, F.A.; Farag, A.; Omar, S.; Khairy, H. Polyhydroxyalkanoates (PHA) from Halomonas Pacifica ASL10 and Halomonas salifodiane ASL11 Isolated from Mariout Salt Lakes. Int. J. Biol. Macromol. 2020, 161, 1318–1328. [Google Scholar] [CrossRef] [PubMed]
  54. Coronado, M.-J.; Vargas, C.; Hofemeister, J.; Ventosa, A.; Nieto, J.J. Production and Biochemical Characterization of an α-Amylase from the Moderate Halophile Halomonas meridiana. FEMS Microbiol. Lett. 2000, 183, 67–71. [Google Scholar] [CrossRef] [PubMed]
Figure 1. Identification of PHB-producing strains that produce PHB. (A) GC analysis comparison of DCW and PHB production in 16 Halomonas strains. (B) Phylogenetic analysis using 16S rRNA sequencing of Halomonas sp. YK44. (C) TEM image of Halomonas sp. YK44 after being cultured for 48 h at 25 °C in MB medium with 2% galactose, final 4% NaCl, and 0.1% yeast extract (Magnification: Right—16,300×, Left—25,000×).
Figure 1. Identification of PHB-producing strains that produce PHB. (A) GC analysis comparison of DCW and PHB production in 16 Halomonas strains. (B) Phylogenetic analysis using 16S rRNA sequencing of Halomonas sp. YK44. (C) TEM image of Halomonas sp. YK44 after being cultured for 48 h at 25 °C in MB medium with 2% galactose, final 4% NaCl, and 0.1% yeast extract (Magnification: Right—16,300×, Left—25,000×).
Polymers 14 05407 g001aPolymers 14 05407 g001b
Figure 2. Optimized carbon and nitrogen sources for PHB production. (A) Comparison of PHB production in MB medium with 2% (w/v) additional carbon sources. (B) Effect of galactose concentration on PHB production. (C) Comparison of PHB production in MB medium with 0.1% (w/v) additional nitrogen sources. (D) Effect of yeast extract concentration on PHB production in MB.
Figure 2. Optimized carbon and nitrogen sources for PHB production. (A) Comparison of PHB production in MB medium with 2% (w/v) additional carbon sources. (B) Effect of galactose concentration on PHB production. (C) Comparison of PHB production in MB medium with 0.1% (w/v) additional nitrogen sources. (D) Effect of yeast extract concentration on PHB production in MB.
Polymers 14 05407 g002aPolymers 14 05407 g002b
Figure 3. Optimized culture conditions for PHB production. (A) Effect of NaCl on PHB production in MB containing 2% (w/v) galactose. (B) Effect of temperature on PHB production in MB with 2% (w/v) galactose. (C) Optimized cultivation time for PHB production at 25 °C in MB with 2% galactose, final 4% NaCl, and 0.1% yeast extract.
Figure 3. Optimized culture conditions for PHB production. (A) Effect of NaCl on PHB production in MB containing 2% (w/v) galactose. (B) Effect of temperature on PHB production in MB with 2% (w/v) galactose. (C) Optimized cultivation time for PHB production at 25 °C in MB with 2% galactose, final 4% NaCl, and 0.1% yeast extract.
Polymers 14 05407 g003aPolymers 14 05407 g003b
Figure 4. PHB production with E. spinosum hydrolysate and optimal pH. (A) Effect of pH on PHB production in MB with 1% galactose in E. spinosum hydrolysate. (B) DCW and PHB production after culture with E. spinosum hydrolysate (C) DCW and PHB production after culture with E. spinosum hydrolysate and activated carbon.
Figure 4. PHB production with E. spinosum hydrolysate and optimal pH. (A) Effect of pH on PHB production in MB with 1% galactose in E. spinosum hydrolysate. (B) DCW and PHB production after culture with E. spinosum hydrolysate (C) DCW and PHB production after culture with E. spinosum hydrolysate and activated carbon.
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Figure 5. Effect of reused sterilized and non-sterilized high salinity medium on total PHB production. Total PHB production in non-sterilized high salinity medium with 2% galactose was compared to production in sterilized high salinity medium with 2% galactose.
Figure 5. Effect of reused sterilized and non-sterilized high salinity medium on total PHB production. Total PHB production in non-sterilized high salinity medium with 2% galactose was compared to production in sterilized high salinity medium with 2% galactose.
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Table 1. PHA synthesis using galactose.
Table 1. PHA synthesis using galactose.
MicroorganismCarbon SourceDCW
(g/L)
PHB Content
(wt%)
PHB
(g/L)
CultureReference
Halomonas halophilaGalactose4.22 ± 0.1080.7 ± 2.03.41 ± 0.12Batch[27]
Halomonas salinaGalactose0.97 ± 0.0312.3 ± 0.480.12 ± 0.01Batch[25]
Halomonas organivoransGalactose5.80 ± 0.2290.55 ± 4.085.61 ± 0.01Batch[25]
Bacillus sp. 112AGalactose1.0235.500.879Batch[26]
Halomonas sp. SF2003Galactose3.16391.23Batch[28]
Table 2. Halomonas strains used in this study.
Table 2. Halomonas strains used in this study.
Similar SpeciesStrainIsolated TemperatureResource Number
1Halomonas alkalicolaDH-1025 °CMABIK MI00000003
2Halomonas cerinaYK4420 °CMABIK MI00000284
3Halomonas sulfidaerisJ05-14M-11R20 °CMABIK MI00000306
4Halomonas fontilapidosiO1225 °CMABIK MI00000338
5Halomonas gomseomensisCJCa10725 °CMABIK MI00000370
6Halomonas arcisCJCbj07825 °CMABIK MI00000396
7Halomonas janggokensisCJCbj08225 °CMABIK MI00000412
8Halomonas salicampiCJCbj04125 °CMABIK MI00000417
9Halomonas lutescensCJCbj05825 °CMABIK MI00000427
10Halomonas fontilapidosiMEBiC1216925 °CMABIK MI00005505
11Halomonas campaniensisS51025 °CMABIK MI00005561
12Halomonas saccharevitansMJ00525 °CMABIK MI00005664
13Halomonas shengliensisMEBiC1209825 °CMABIK MI00005446
14Halomonas denitrificansMEBiC1332825 °CMABIK MI00005839
15Halomonas aestuariiMEBiC1336925 °CMABIK MI00005871
16Halomonas lutea15A02127 °CMABIK MI00005926
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Jung, H.J.; Kim, S.H.; Cho, D.H.; Kim, B.C.; Bhatia, S.K.; Lee, J.; Jeon, J.-M.; Yoon, J.-J.; Yang, Y.-H. Finding of Novel Galactose Utilizing Halomonas sp. YK44 for Polyhydroxybutyrate (PHB) Production. Polymers 2022, 14, 5407. https://doi.org/10.3390/polym14245407

AMA Style

Jung HJ, Kim SH, Cho DH, Kim BC, Bhatia SK, Lee J, Jeon J-M, Yoon J-J, Yang Y-H. Finding of Novel Galactose Utilizing Halomonas sp. YK44 for Polyhydroxybutyrate (PHB) Production. Polymers. 2022; 14(24):5407. https://doi.org/10.3390/polym14245407

Chicago/Turabian Style

Jung, Hee Ju, Su Hyun Kim, Do Hyun Cho, Byung Chan Kim, Shashi Kant Bhatia, Jongbok Lee, Jong-Min Jeon, Jeong-Jun Yoon, and Yung-Hun Yang. 2022. "Finding of Novel Galactose Utilizing Halomonas sp. YK44 for Polyhydroxybutyrate (PHB) Production" Polymers 14, no. 24: 5407. https://doi.org/10.3390/polym14245407

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