Abstract
Streptococcus agalactiae is a highly pathogenic bacterium of aquatic species and terrestrial animals worldwide, whereas chitin and its derivative chitosan are among the most abundant biopolymers found in nature, including the aquatic milieu. The present investigation focused on the capability of S. agalactiae to degrade and utilize these polymers. Growth of S. agalactiae in the presence of colloid chitin, chitosan, or N‐acetyl‐glucosamine (GlcNAc) was evaluated. Chitosanase production was measured daily over 7 days of growth period and degraded products were evaluated with thin later chorography. Chitin had no effect on the growth of S. agalactiae. Degraded chitin, however, stimulated the growth of S. agalactiae. S. agalactiae cells did not produce chitinase to degrade chitin; however, they readily utilize GlcNAc (product of degraded chitin) as sole source of carbon and nitrogen for growth. Chitosan at high concentrations had antibacterial activities against S. agalactiae, while in the presence of lower than the inhibitory level of chitosan in the medium, S. agalactiae secrets chitosanase to degrade chitosan, and utilizes it to a limited extent to benefit growth. The interaction of S. agalactiae with chitin hydrolytes and chitosan could play a role in the diverse habitat distribution and pathogenicity of S. agalactiae worldwide.
Keywords: aquaculture, chitin, chitosan, chitosanase, diseases, Streptococcus
1. INTRODUCTION
Streptococcosis is caused by gram‐positive, globally distributed bacteria capable of infecting more than 27 species of fish inhabiting fresh, brackish, and marine waters (Bowater et al., 2012; Chou et al., 2014; Keirstead et al., 2014; Klesius, Shoemaker, & Evans, 2008; Sheehan et al., 2009). Streptococcus agalactiae in particular not only causes invasive disease in fish but also poses a zoonotic hazard. Some strains of aquatic S. agalactiae have potential for pathogen transmission between aquatic animals and humans (Delannoy et al., 2013). S. agalactiae‐induced streptococcosis causes substantial fish mortalities and large economic losses on aquaculture operations worldwide, particularly in farmed tilapia (Oreochromis sp.), rainbow trout (Oncorhynchus mykiss), grouper (Epinephelus lanceolatus), and hybrid striped bass (Morone chrysops X M. saxatilis) (Shoemaker, Xu, Garcia, & LaFrentz, 2017; Shoemaker, Xu, & Soto, 2017). Outbreaks of streptococcosis have also been described in wild fish, e.g., in mullet in Kuwait bay (Evans et al., 2008; Jafar et al., 2008) and in giant Queensland grouper and other wild fish in Australia (Bowater et al., 2012). Other aquatic or semiaquatic species such as marine mammals (Evans et al., 2008; Zappulli et al., 2005), crocodiles (Bishop et al., 2007), bullfrogs (Amborski, Snider, Thune, & Culley, 1983), and terrestrial mammals such as cattle, dogs, cats (Brochet et al., 2006; Sørensen, Poulsen, Ghezzo, Margarit, & Kilian, 2010), and humans were reportedly susceptible to S. agalactiae infection. In humans, S. agalactiae was found to colonize the rectovaginal tract and cause neonatal infectious disease (Manning et al., 2009; Phares et al., 2008) and may also cause meningitis, septicemia, as well as localized infections (Chaiwarith et al., 2011). The drivers behind the emergence of S. agalactiae disease in humans and other animals are still poorly understood.
As an autochthonous bacterium of diverse aquatic ecosystems, the interaction between S. agalactiae and chitin is of interest; particularly as chitin is one of the most abundant biopolymers in aquatic environments. Indeed, each year more than one billion tons of chitin is produced in the biosphere by many organisms, mainly by insects, fungi, crustaceans, and other marine and freshwater organisms (Gooday, 1990). Chitin consists of unbranched and degradable chains of β (1,4)‐linked N‐acetyl‐glucosamine (GlcNAc) residues and is part of the cell wall structure in invertebrates, protozoa, fungi, and certain groups of algae (Flach, Pilet, & Jolles, 1992). Relatedly, chitosan is a collective name for a group of partially or fully deacetylated chitin, although the degree of the N‐deacetylation is almost never complete (Rabea et al., 2003). In nature, the polymer is partially acetylated and, in fact, the name chitosan describes a wide range of polymers with randomly distributed various proportions of D‐glucosamine (GlcN) (deacetylated unit) and N‐acetyl‐D‐glucosamine (acetylated unit) residues (Pelletier & Sygusch, 1990). Chitosan is also found in the cell wall of several fungi (Pochanavanich & Suntornsuk, 2002), in the green algae Chlorella sp. (Mihara, 1961), yeast, protozoa, and in insect cuticles (Aruchami, Gowri, & Sundara‐Rajulu, 1986).
Among bacteria, chitin also provides necessary carbon and nitrogen sources for energy metabolism. Except for Serratia marcescens, which is one of the best‐studied chitinolytic bacteria (Vaaje‐Kolstad, Horn, Sørlie, & Eijsink, 2013), many aquatic bacteria such as Vibrio sp. can live solely on chitin (Rathore & Gupta, 2015). Recently, a hypervirulent fish strain of Aeromonas hydrophila was found to use chitin and chitosan (partially deacetylated chitin) as sole carbon sources for growth (Zhang, Xu, Qiu, & Beck, 2017). Accordingly, the enormous amounts of chitin/chitosan production and continuous deposition of these highly insoluble polymers in the biosphere are degraded by chitinase and chitosanase (GIA, 2010). Chitinase (EC 3.2.1.14) and chitosanase (EC 3.2.1.132) are two members of the glycoside hydrolase family and are characterized by their ability to catalyze the hydrolytic cleavage of chitin and chitosan, respectively (Dahiya, Tewari, & Hoondal, 2006). Chitinase catalyzes the degradation of chitin and these enzymes detected in a wide variety of organisms including bacteria, fungi, viruses, plants and insects (Gooday, 1990; Henrissat & Davies, 1997; Keyhani & Roseman, 1997; Saito et al., 1999). Chitosanase or GlcN‐ase is a hydrolytic enzyme acting on β‐1,4‐glycosidic linkage of chitosan to release chito‐oligosaccharides (Liu et al., 2009). Several microorganisms including actinomycetes, fungi, and bacteria as well as some plants have been reported to produce chitosanase to degrade chitosan and were able to use chitosan as a sole carbon source (Lee et al., 1996; Shimosaka, Nogawa, Wang, Kumehara, & Okazaki, 1995) including Sphingomonas sp. (Zhu, Zhou, & Feng, 2007), and Bacillus sp. (Choi, Kim, Piao, Yun, & Shin, 2004; Kurakake, Yo‐u, Nakagawa, Sugihara, & Komaki, 2000; Zakaria, Zakaria, Musa, Hamilin, & Zulkifly, 2012). The chitin‐degrading enzyme (chitinase) in Yersinia entomophaga functions as an integral part of toxin complex (Busby et al., 2012). For V. cholerae, its association with chitin was related with its chemotaxis, cell multiplication, induction of competence, biofilm formation, as well as pathogenicity for humans and aquatic animals (Pruzzo, Vezzulli, & Colwell, 2008).
Because of the diverse habitat distribution of S. agalactiae and global abundance of chitin/chitosan as a major component of organic matter in aquatic ecosystems, elucidating their interactions will augment our understanding of these bacteria and potentially guide the development of preventatives and therapeutic approaches for disease control. Therefore, the purpose of this study was to examine the in vitro interactions of S. agalactiae with chitin, chitosan, and their hydrolysis products to reveal new clues aimed at minimizing disease outbreaks of these globally important bacterial pathogens.
2. MATERIALS AND METHODS
2.1. Bacterial strain and culture conditions methods
The strain, TN‐Hon‐084 of Streptococcus agalactiae (Shoemaker, Xu, et al., 2017; Shoemaker, Xu, & Soto, 2017) originally isolated from diseased fish, was used in this study. The bacterium was routinely cultured and maintained in tryptic soy broth (TSB) (Fisher Scientific, Pittsburgh, PA) at 28°C.
2.2. Colloidal chitin and chitosan preparation
Colloidal chitin was prepared according to the method of Murthy and Bleakley (2012) with some modifications. Briefly, 1 g chitin powder from shrimp shells (Sigma–Aldrich, St. Louis, MO) was dissolved in 15 ml concentrated hydrochloric acid (HCl) and vigorously stirred for 1 hr in a chemical fume hood at room temperature. Chitin was precipitated as a colloidal suspension by adding 250 ml distilled water. Aliquots of the chitin suspension were dispensed in 50 ml tubes and centrifuged at 4000 rpm for 10 min. Precipitates were washed 3 × with distilled water. The pH was adjusted to 5.5 with NaOH. The concentration of colloidal chitin was adjusted to 30 mg/ml. The preparation was then autoclaved at 121°C for 15 min and stored at 4°C until use.
Chitosan (CS) was purchased from Sigma–Aldrich (St. Louis, MO). Chitosan stock solution was prepared by dissolving in 0.2 N HCl at a concentration of 1% (w/v) with stirring overnight at 30°C. The pH of the solution was then adjusted to 5.5 with NaOH. Stock solution of 0.2N HCl (chitosan solvent) was prepared and pH was adjusted to 5.5 to determine the effect of HCl. Stock solutions were sterilized at 121°C for 15 min in an autoclave and stored at 4°C after cooling.
2.3. Effect of colloid chitin on growth of Streptococcus agalactiae
The effect of colloid chitin on the growth of S. agalactiae and the ability of S. agalactiae to use colloid chitin as a sole carbon source to grow were assessed using TSB and M9 minimal medium (MM) solution supplemented with 0.6% colloid chitin. The MM contained 47.8 mM Na2HPO4, 22.0 mM KH2PO4,8.5 mM NaCl,18.7 mM NH4Cl, 20 mM MgSO4 and 0.1 mM CaCl2. To prepare working solution, 20 ml 5× minimal salts, 400 μl of 1M MgSO4 and 200 μl of 0.1M CaCl2 was added and made up to 100 ml. Stock solutions were sterilized at 121°C for 15 min in an autoclave. Growth media (TSB or MM) without colloid chitin served as controls. Approximately 2 × 108 colony forming units (CFU)/ml of S. agalactiae were washed with MM, and inoculated to 50 ml of growth medium, resulting in the start cell density of 4 × 107 CFU/ml. The culture was kept at 28°C with constant shaking at 130 rpm. An aliquot of 100 μl of culture was sampled daily for 4 days and numbers of CFU were determined by conventional plate count method using tryptic soy agar (TSA) as growth medium.
2.4. Preliminary chitinase activity assay
Extracellular chitinolytic activity of S. agalactiae was evaluated by applying cell culture on agar medium containing colloidal chitin. Aliquots of 10 μl of the bacterial culture were spotted on the surface of MM agar containing 0.2% colloid chitin. Two plates were used, with each plate having three spots. Plates were incubated at 28°C until halo zones (clearing of opaque medium) formed around the colonies. Aeromonas hydrophila, ML‐10‐51K, which is known for having chitinolytic activity, was used as a positive control (Zhang, Bland, Xu, & Chung, 2015; Zhang et al., 2017).
2.5. Growth of bacteria in M9 minimal medium containing N‐acetyl‐D‐glucosamine (GlcNAc) or chitosan (CS) as sole carbon sources
Kinetic growth was assayed by measuring the turbidity of a cell suspension in 96‐well microtiter plates. Bacteria were grown in M9 minimal media, supplemented with various concentrations of GlcNAc or CS, and no carbon source served as control. Overnight culture of bacterial cells was centrifuged and resuspended in M9 minimal medium, and the optical density was adjusted to OD540 = 0.3. Aliquots of 125 μl bacterial suspension were added to each well of a 96‐well plate. Then, 250 μl GlcNAc or CS with concentrations varied from 0.125 to 4% and from 0.003 to 0.1%, respectively, was added to each well. Wells without addition of GlcNAc or CS served as controls. There were quadruplicate replicate wells for each concentration. Kinetic of bacterial growth in various concentrations of GlcNAc or CS were measured at 28°C with constant shaking for 30 and 72 hr, respectively, using an Epoch‐2 microplate reader (BioTek, Winooski, TX, USA).
2.6. Coculture of Streptococcus agalactiae with an extracellular chitinase‐producing aquatic bacterium
To determine if S. agalactiae was capable of scavenging chitin degraded products produced by other chitinolytic bacterium, S. agalactiae was cocultured with Aeromonas hydrophila ML‐10‐51K. Overnight cultures of S. agalactiae and A. hydrophila were washed with MM medium and inoculated individually or together in MM medium (final volume of 2.5 ml) containing 0.6% colloid chitin. Disappearance of colloidal chitin from the test tubes was daily inspected for 5 days. Samples were centrifuged at 3000 rpm for 10 min and remaining levels of colloid chitin in test tubes were photographed.
To obtain extracellular chitinolytic enzyme, A. hydrophila was cultured in M9 minimal medium in 50 ml tubes containing 0.6% colloid chitin (after washing once with MM) until all the chitin disappeared. Cell‐free culture supernatant was obtained by centrifugation at 5000 rpm for 15 min and filtered through a 0.22 μm Millipore® filter. The filter‐sterilized supernatant was divided to two parts and one part was heated at 100°C for 30 min to inactivate chitinolytic enzymes. The cell‐free supernatant with active or inactivated chitinase and minimal medium (2.5 ml) were then supplemented with 0.6% colloid chitin. M9 minimal medium without colloid chitin served as control. Cells of S. agalactiae washed with MM medium, were inoculated with starting cell density of approximately 3 × 107 CFU/ml. MM medium supplemented with same level of colloid chitin was also inoculated with S. agalactiae. The culture was kept at 28°C with constant shaking at 130 rpm. An aliquot of 100 μl of culture was sampled daily for 4 days and numbers of CFU were determined using the same method described above.
2.7. Effect of chitosan on bacterial cell proliferation
Cell proliferation assays were conducted by measuring the turbidity of cell suspensions in 96‐well microtiter plates. The bacterial culture (OD540 = 1.0) were serially diluted at 1 to 1,000 ratio in TSB. A total volume of 125 μl bacterial suspension in triplicate was added to each well (except first row) of a 96‐well plate. A total volume of 250 μl chitosan or HCl at a concentration of 0.8% in bacterial suspensions was added to first row. Serial twofold dilutions of chitosan or HCl made in bacterial suspension to give final chitosan concentrations of 0.8, 0.4, 0.2, 0.1, 0.05, 0.025, and 0% (w/v). Negative controls (chitosan + TSB or HCl + TSB) were also assayed in triplicate. Kinetics of bacterial growth were measured at 28°C with constant shaking for 24 hr using an Epoch‐2 microplate reader (BioTek, Winooski, TX). Absorbance values of negative controls were subtracted from the corresponding sample absorbance readings. After incubation, subsamples from each concentration were strike in TSB agar plates containing no CS or HCl to test bacterial recovery (i.e., to determine whether viable cells were present). The samples were re‐incubated at 28°C for 24–72 hr and the growth of bacterial colonies was observed.
2.8. Bacterial cell viability
The amounts of viable bacteria in each well were determined using an assay of MTT (3‐(4,5‐dimethylthiazol‐2‐yl)‐2,5‐diphenyl‐2H‐tetrazolium bromide (Sigma‐Aldrich (St. Louis, MO). A stock MTT solution (5 mg/ml) in phosphate‐buffered saline (PBS), pH 7.4 was prepared immediately prior to use, and filter‐sterilized with a 0.22 μm Millipore® filter. Three sets of bacterial culture in 96‐well microtiter plates (one for each time course, 24, 48, and 72 hr incubation), identical to above, were prepared and incubated at 28°C for 20, 44, and 68 hr. The MTT stock solution was then added to each well at a final concentration of 0.5 mg/ml, and the mixture was incubated at 28°C for 4 hr. The formazan produced was solubilized by addition of 125 μl acidified isopropanol (0.04N HCl in isopropanol). The quantity of dissolved formazan (presumably directly proportional to the number of viable cells) was measured at 570 nm using an Epoch‐2 microplate reader.
2.9. Culture conditions for production of chitosanase
To produce chitosanase, the pre‐grown bacteria were inoculated in 35 ml M9 minimal medium containing 0.05% chitosan and grown in an orbital shaking incubator (130 rpm) for 7 days at 28°C. Daily, cell viability was estimated by using MTT assay as described above and 4 ml of subsamples centrifuged and resulting supernatants were saved at −20°C until use for measuring enzyme activities.
2.10. Assessment of chitinase and chitosanase activities in extracellular products (ECP)
Chitinase activity was measured with colloidal chitin as a substrate by measuring the amount of the reducing end group, NAG, degraded from colloidal chitin, as described by Imoto and Yagishita (1971) with some modifications. The chitosanase activities were determined by measuring the amount of N‐acetyl‐D‐glucosamine (GlcNAc) or glucosamine (GlcN) degraded from chitin and chitosan, respectively. Briefly, corresponding crude enzymes in ECP (0.9 ml) were mixed at 3:1 ratio with 2% colloidal chitin or 1% chitosan. After incubation for 2 hr at 37°C for chitinase and 56°C for chitosanase, the reaction mixture was subjected to refrigerated centrifugation (4°C) at 13,000 rpm for 10 min. The resulting supernatant (0.7 ml) was mixed with 70 μl of 0.1% NBT solution and boiled for 20 min. The NBT solution was made by dissolving 0.1 g NBT in 50 ml 0.05M NaOH and mixing with equal volume of 0.5 M sodium potassium tartrate. (Both solutions were filtered through a 0.22 μm Millipore® filter before mixing). After cooling, the absorbance of the mixture was measured at 660 nm using an Epoch‐2 microplate reader. The activity was calculated from a standard curve obtained using NAG or glucosamine. One unit (U) of the enzyme (chitinase or chitosanase) activity was defined as the amount of enzyme that yield 1 μmol of reducing sugar as N‐acetyl‐D‐glucosamine (GlcNAc) or glucosamine (GlcN) equivalent per minute.
2.11. Thin layer chromatography (TLC)
Chitosan hydrolysis was qualitatively analyzed by means of TLC using silica gel plate (DC Kieselgel 60, Merck KGaA). ECP‐mediated chitosanase enzyme was obtained from the cultures described above in the culture conditions for production of chitosanase by centrifugation at 5000 rpm for 30 min. The resulting supernatant (3 ml) was filtered through a 0.22 m filter (PES membrane) unit (Millex‐GP, Merck Millipore Ltd, Tullagreen, IRL) to remove remaining bacterial cells and concentrated to a volume of approximately 0.5 ml using a Pierce Concentrator (PES, 20k MWCO; Thermo Scientific, Rockford, IL). The concentrated supernatant (0.5 ml) was mixed at 3:1 ratio with 1% chitosan. After incubation for 24 hr at 37°C, the reaction mixture was subjected to refrigerated centrifugation at 13,000 rpm for 10 min.
TLC was performed to analyze ECP‐mediated chitosanase enzyme using modified method of Bond, Tsai, and Russell (1999). Briefly, an aliquot of 2–6 μl of samples was spotted on a TLC plate. Chromatography was developed in a solvent containing ethyl acetate:butanol:acetic acid:water (80:10:5:5, v/v) for 90 min. The plate was allowed to air‐dried and stained by spraying with p‐anisaldehyde reagent (p‐anisaldehyde: ethanol:sulfuric acid:acetic acid; 1:18:0.5:0.5, v/v) and heated at 120°C for 5 min.
2.12. Statistical analysis
Graphs and standard error of means (SEM) of the data were performed using Graphpad Prism 6.0 (San Jose, CA, USA).
3. RESULTS
Colloidal chitin had no influence on the growth of Streptococcus agalactiae in either TSB (Figure 1a) or M9 minimal medium (Figure 1b). Preliminary tests showed that clear hydrolysis zones formed around Aeromonas hydrophila ML‐10‐51K colonies, which was used as a positive control, on colloidal chitin agar. However, S. agalactiae did not form such hydrolytic zones. We also analyzed chitinase enzyme activities in cell‐free culture supernatants of S. agalactiae incubated with colloid chitin medium. Similarly, S. agalactiae did not excrete detectable levels of chitinase to hydrolyze colloid chitin (data are not shown).
Figure 1.

Effect of colloid chitin (CC) on growth of Streptococcus agalactiae TN‐Hon‐084 in growth medium (tryptic soy broth, TSB) (a) or M9 minimal medium (MM) (b) for 4 days. Error bars represent standard error of means (SEM) from three replicates
Even though, they did not produce chitinolytic enzymes to hydrolyze chitin, we next cocultured S. agalactiae with a chitinase‐producing bacterium (A. hydrophila ML‐10‐51K) to test if S. agalactiae can coexist and scavenge degraded products produced by other chitinolytic bacteria. Apparently, S. agalactiae was able to grow in the coculture even though it could not degrade colloid chitin itself (Figure 2a). Colloid chitin disappeared slightly faster in coculture compared to sole culture of chitinase‐producing bacterium. In the cell‐free culture supernatant of A. hydrophila grown in medium containing colloid chitin as a sole carbon source, the number of S. agalactiae cells increased up to 2 days (CFU increased from 1.3x108 to 1.6x108) and then, constantly decreased over the next 4 days (Figure 2b). The number of cells remained constant for 2 days in the cell‐free culture supernatant containing inactivated chitinolytic enzyme suggesting presence of degraded chitin. There was a linear decrease in the number of colony counts in the control groups.
Figure 2.

Amount of colloid chitin left after culturing Streptococcus agalactiae TN‐Hon‐084 with or without Aeromonas hydrophila ML‐10‐51K in minimal medium for 10 days. Tube 1—Coculture of S. agalactiae and A. hydrophila and; Tube 2—A. hydrophila alone; Tube 3— S. agalactiae alone; Tube 4—Colloid chitin alone (a). Influence of cell‐free culture supernatant of A. hydrophila ML‐10‐51K containing chitinolytic enzyme on growth of S. agalactiae TN‐Hon‐084 in M9 minimal medium (MM) containing colloid chitin (CC) for 6 days (b). Error bars represent standard error of means (SEM) from three replicates
The growth curve in M9 minimal media containing various concentrations of GlcNAc as a sole carbon source was conducted to test if they can utilize the monomeric unit of the polymer chitin (Figure 3). Log phase was longer in bacteria with higher levels of GlcNAc in the medium. S. agalactiae incubated in medium containing 1% and 2% GlcNAc reached to stationary phase after 16 and 40 hr of incubation, respectively. S. agalactiae cultured in medium containing 4% and 8% GlcNAc was still on log phase at 72 hr of incubation. At the end of the 72‐hr incubation period, absorbance reading was increasingly higher with increasing concentration of GlcNAc in the culture medium up to 4%.
Figure 3.

Kinetic growth of Streptococcus agalactiae TN‐Hon‐084 in M9 minimal medium containing various concentrations of N‐acetyl‐D‐glucosamine (GlcNAc) as a sole carbon source. Relative cell growth determined by the turbidity measured at OD 540 nm. Data are presented as mean ± standard deviation (SD) from three replicates
Chitosan exhibited antibacterial activity at the concentration of 0.2% or higher against S. agalactiae (Figure 4a,b). On the other hand, absorbance reading of chitosan‐treated groups at the concentrations of 0.1% and lower was higher than that of the control group (Figure 4a). It completely inhibited growth of S. agalactiae at the concentration of 0.4% (w/v) over a 72‐hr incubation period based on MTT assay. Chitosan at a concentration of 0.1% had the highest reading regardless of the exposure time. In the medium containing 0.2% chitosan, growth of both bacteria was strongly inhibited up to 24‐hr incubation period. After 48‐hr incubation, however, there were no differences in the absorbance values of S. agalactiae between chitosan‐treated groups (0.2%, w/v) and untreated controls. The effect of HCl as a chitosan solvent was also evaluated at the same concentrations used in chitosan‐treated groups on the relative survival at 24, 48, and 72 hr with S. agalactiae. No antibacterial activity of HCI was observed against on growth and survival of bacterium (Figure 4b).
Figure 4.

The kinetic growth (a) and relative cell viability (survival) (b) of Streptococcus agalactiae TN‐Hon‐084 incubated with various concentrations of chitosan. Relative cell growth determined for 24 hr with 1‐hr interval by the turbidity measured at OD 540 nm. Cell viability was estimated by MTT assay and absorbance was measured at OD 570 nm in 96‐well plates following 24‐, 48‐, or 72‐hr exposure to chitosan. Data are presented as mean ± standard deviation (SD) from three replicates. All experiments were performed duplicate
To monitor chitosan utilization by S. agalactiae as a sole carbon source, growth curves in minimal medium containing gradient levels of chitosan were determined (Figure 5). Absorbance readings of all chitosan‐treated groups from 0.006% to 0.1% were markedly higher than that of the control group. Absorbance reading of control group remained unchanged throughout the incubation period. At the end of the 72‐hr incubation period, cell densities in medium containing chitosan concentration from 0.125% to 0.1% were similar and reached stationary phase at 60 hr of incubation.
Figure 5.

Kinetic growth of Streptococcus agalactiae TN‐Hon‐084 in M9 minimal medium containing various concentrations of chitosan as a sole carbon source. Relative cell growth determined by the turbidity measured at OD 540 nm. Data are presented as mean ± standard deviation (SD) from three replicates
Time course of chitosanase productions by S. agalactiae correlated with the viable bacterial cells as shown in Figure 6. Cultivation of S. agalactiae cells in a M9 medium supplemented with 0.05% chitosan as a sole carbon source excreted chitosanase into the culture medium. The level of extracellular chitosanase produced by S. agalactiae and the amount of viable bacterial cells increased with increasing the incubation time up to day 6 and day 5, respectively. This point further, the level of chitosanase in the medium remained unchanged in contrast to decreasing amount of surviving bacterial cells. The low growth of bacteria at day 2 in the medium containing chitosan was due to the inhibitory activity of chitosan on bacterial growth. After day 3, constant increase of the relative ratio of chitosanase to amount of live bacteria in the medium was observed throughout the cultivation period.
Figure 6.

Chitosanase activity compared to relative cell viability (survival) of Streptococcus agalactiae TN‐Hon‐084 incubated in liquid M9 minimal medium 0.05% chitosan at 28°C for 8 days. Data are presented as mean ± standard deviation (SD) from three replicates
The hydrolytic ability of extracellular products (ECP) from S. agalactiae was analyzed using thin layer chromatograph (TLC) (Figure 7). When ECP from stimulated S. agalactiae for chitosanase production was incubated with chitosan as substrate for 2 hr at 37°C, various lengths of chitosan oligosaccharides were liberated from chitosan. On the other hand, no detectable degradation products were observed in ECP of unstimulated bacteria during growth (lane 4). ECP from S. agalactiae grown in minimal medium in the presence of chitosan to stimulate chitosanase production for 8 days alone revealed remaining of shorter chained oligosaccharide from cleavage of chitosan. No degradation product was detected in control (chitosan without ECP (lane 1).
Figure 7.

Thin layer chromatograph (TLC) of chitosan‐degrading products by extracellular products (ECP) of Stroptococcus agalactiae TN‐Hon‐084. Lane 1. Chitosan alone (not treated with ESP); Lane 2. Chitosan treated with ECP from S. agalactiae; Lane 3. ECP from S. agalactiae cultured in chitosan containing medium; and Lane 4. ECP from S. agalactiae cultured in TSB without chitosan
4. DISCUSSION
Chitin and chitosan are abundant biomaterials. Chitin is the second most abundant polymers on earth after cellulose and possibly the most abundant in the aquatic environment. Although chitosan is commercially produced from shrimp and crab shell by deacetylation of chitin with strong alkalis at high temperatures for long periods of time (Knorr, 1991), it is also found in nature including the cell walls of several fungi (Pochanavanich & Suntornsuk, 2002), in the green algae Chlorella sp. (Mihara, 1961), and in yeast, protozoa, and insect cuticles (Aruchami et al., 1986). In aquatic environments, available chitosan may provide S. agalactiae with sources of nutrients and energy. From the present results, there was no evidence that S. agalactiae can degrade chitin. However, it thrived on degraded chitin products without investing energy in the biosynthesis of this enzyme. During growth, chitin disappeared faster from medium containing both bacterial species than that containing only the chitin‐degrading strain (A. hydrophila). It was assumed that cells with no apparent chitinase activity fed on hydrolytic products generated in excess by the chitinase‐positive populations. This type of multicellular cooperation could be a strategy observed in bacterial communities (Shapiro, 1998) and has been described for several chitinolytic strains (Chernin et al., 1998; DeAngelis, Lindow, & Firestone, 2008; Gaffney et al., 1994).
Several culture independent studies in aquatic environments that quantify the fraction of chitin degraders vs. chitin consumers in the total bacterial community support the existence of significant cross feeding during chitin degradation: chitinolytic organisms were estimated to represent average about 1% of all prokaryotes in a variety of aquatic ecosystems (Beier, Jones, Mohit, Hallin, & Bertilsson, 2011; Cottrell, Moore, & Kirchman, 1999). An even lower fraction of cells displayed active chitinolytic activity in natural aquatic habitats (Beier & Bertilsson, 2011; Beier et al., 2012). S. agalactiae is incapable of degrading chitin but can utilize N‐acetyloglucosamine as the sole source of carbon and nitrogen. Mobley, Doyle, Streips, and Langemeier (1982) found that when GlcNAc was used as a sole carbon source, N‐acetylglucosamine sugar was utilized in cell macromolecular synthesis and energy metabolism; However, if GlcNAc did not serve as the sole source of carbon, then ~90% of GlcNAc taken up into the cells was in turn incorporated into the cell walls in the Bacillus subtilis (Mobley et al., 1982). The ability to take up GlcNAc appears to be widespread in aquatic bacteria (Beier & Bertilsson, 2011; Eckert, Baumgartner, Huber, & Pernthaler, 2013; Nedoma, Vrba, Hejzlar, Šimek, & Straškrabová, 1994; Riemann & Azam, 2002).
The antibacterial activity of chitosan and its derivatives has been recognized against bacteria, (Benhabiles et al., 2012; Kong, Chen, Xing, & Park, 2010; Liu, Du, Wang, & Sun, 2004; No, Park, Lee, & Meyers, 2002; Sudarshan, Hoover, & Knorr, 1992; Wei & Xia, 2003; Xia, 2003; Yang, Chou, & Li, 2005; Zheng & Zhu, 2003), fungal, and/or viral pathogens (Hirano & Nagao, 1989; Uchida, Lzume, & Ohtakara, 1989). Similar activities have been reported for food bacteria, mold, and yeast (Benhabiles et al., 2012; No et al., 2002; Wei & Xia, 2003). Recently, we demonstrated that chitosan and its derivatives inhibited the growth of three pathogenic gram‐negative bacteria of warm water finfish (Yildirim‐Aksoy & Beck, 2017). In the present study, the antibacterial activities of chitin and chitosan were also examined against S. agalactiae. Colloidal chitin had no effect on growth of the S. agalactiae; however, at concentrations of 0.2% or higher, chitosan inhibited the growth of this bacterium. By examining relative antibacterial activities of chitin, chitosan, and its oligomers against four gram‐positive and seven gram‐negative bacteria by Benhabiles et al. (2012), they found that chitosan exhibited a bacteriostatic effect on the gram‐negative bacteria, Escherichia coli ATCC 25922, Vibrio cholerae, Shigella dysenteriae, and Bacteroides fragilis but not against Salmonella typhimurium. The antibacterial mechanism of chitosan is mainly acting on the outer surface of bacteria by binding to the oppositely charged bacterial surface to cause agglutination. Its interaction with the membrane of the cell alters cell permeability causing leakage of cytoplasmic components and finally death of the cell (Yildirim‐Aksoy & Beck, 2017). A probable explanation for the stimulated growth with the low chitosan‐treated groups is that there was insufficient polysaccharide to interact and kill all the bacteria in the culture medium and the amino groups of chitosan were bound to cell debris or surface components of the bacteria and were no longer available to attach to other cell surfaces. Therefore, surviving S. agalactiae cells continued reproducing and possessed the ability to degrade and utilize chitosan to benefit their growth. Several microorganisms including actinomycetes, fungi, and bacteria have been reported to produce chitosanase to degrade chitosan and use it as a sole carbon source (Lee et al., 1996; Shimosaka et al., 1995). Chitosan‐degrading bacteria have been identified in Sphingomonas sp. (Zhu et al., 2007) and Bacillus sp. (Choi et al., 2004; Kurakake et al., 2000; Zakaria et al., 2012).
Even though, being not capable of producing chitinase to degrade chitin, S. agalactiae secretes chitosanase into surrounding medium in response to chitosan induction. The distinction between chitinases and chitosanases is that chitinase specifically cleaves the N‐acetyl‐D‐glucosaminidic bonds while chitosanase cleaves the β‐D‐glucosaminidic bonds. Chitosanases can hydrolyze all kinds of linkages in chitosan except for the GlcNAc‐GlcNAc bond (Zhu, Wu, & Dai, 2003). However, some chitinases hydrolyze GlcN‐GlcNAc bonds in addition to GlcNAc‐GlcNAc ones. Apparently, S. agalactiae required chitosan to induce the production of chitosanase (Figure 7). While some microorganisms constitutively produced chitosanase without chitosan, most microorganisms needed chitosan as an inducer to produce chitosanase (Kurakake et al., 2000; Lee et al., 1996; Shimosaka et al., 1995). In this study, S. agalactiae was investigated for secretion of chitosanase during its growth. The changes of chitosanase in the culture supernatant were analyzed for 8 days in chitosan medium and correlated with the viable bacterial cells. It showed that S. agalactiae produced extracellular chitosanase continuously and increased steadily during the exponential phase of growth when growth medium containing 0.05% chitosan as substrate. The highest level of chitosanase was found on the sixth day of culture when the bacterium entered the late stationary phase, then it remains unchanged although cell count was gradually declined. This result may be due to the accumulation of chitosanase in the medium during previous growth phase. The low growth of bacteria at second day in the medium containing chitosan may be due to the inhibitory activity of chitosan on bacterial growth.
In gram‐positive bacteria, peptidoglycan makes up as much as 90% of the thick cell wall enclosing the plasma membrane. The peptidoglycan layer in the bacterial cell wall is formed from linear chains of two alternating amino sugars, namely N‐acetylglucosamine (GlcNAc) and N‐acetylmuramic acid (MurNAc). Chitosan is a linear polysaccharide composed of randomly distributed β‐(1→4)‐linked D‐glucosamine (deacetylated unit) and N‐acetyl‐D‐glucosamine (acetylated unit). Chitin and chitosan are distinguished by the amount of acetylation of the D‐glucosamine (GlcN) residues. S. agalctiae, a gram‐positive bacterium, might be using N‐acetyl‐glucosamine (GlcNAc) residues of chitin and acetylated units of chitosan to build the peptidoglycan layer in their cell walls. The bacterium was able to decompose chitosan and utilize D‐glucosamine as additional source of carbon to grow when cells are grown in the growth media (TSB) containing less than inhibitor levels of chitosan. When chitosan was used as the sole carbon source, however, the bacterium can utilize it to a certain extent. Increasing chitosan level did not further stimulate growth of cells. This might be explained by limited levels of acetyl groups in chitosan compared to GlcNAc. This relates to the fact that polymers containing more than 70% acetylating are considered chitin, while those with <30% are called chitosan.
In conclusion, S. agalactiae did not possess the ability to degrade chitin but readily utilized degraded chitin products for growth. The bacterium utilized GlcNAc as the only source of carbon and nitrogen. Colloidal chitin has no effect on growth of S. agalactiae, however, chitosan at concentrations of 0.2% or higher, inhibited the growth of S. agalactiae. Lower inhibitory level of chitosan, on the other hand, stimulates the growth of the bacterium. In the presence of chitosan in the medium, S. agalactiae secreted chitosanase to degrade chitosan, and utilized to limited extent to benefit its growth. The interaction of S. agalactiae with chitin hydrolytes and chitosan plays a role in diverse habitat distribution of S. agalactiae worldwide.
CONFLICT OF INTEREST
All authors certify that there is no conflict of interest with any financial/research/academic organization. Mention of trade names or commercial products in this article is solely for the purpose of providing specific information and does not imply recommendation or endorsement by the U.S. Department of Agriculture.
AUTHOR CONTRIBUTION
Yildirim‐Aksoy designed and carried out the experiment and wrote the manuscript with support from Beck and Zhang. All authors discussed the results and commented on the manuscript.
ETHICAL APPROVAL
Not applicable.
ACKNOWLEDGMENTS
The authors thank reviewers for their time and constructive comments.
Yildirim‐Aksoy M, Beck BH, Zhang D. Examining the interplay between Streptococcus agalactiae, the biopolymer chitin and its derivative. MicrobiologyOpen. 2019;8:e733 10.1002/mbo3.733
DATA ACCESSIBILITY
All data generated or analyzed during this study are included in this published article.
References
- Amborski, R. L. , Snider, T. G. , Thune, R. L. , & Culley, D. D. (1983). A non‐hemolytic, group B Streptococcus infection of cultured bullfrogs, Rana catesbeiana, in Brazil. Journal of Wildlife Diseases, 19, 180–184. 10.7589/0090-3558-19.3.180 [DOI] [PubMed] [Google Scholar]
- Aruchami, M. , Gowri, N. , & Sundara‐Rajulu, G. (1986). Chitin deacetylases in invertebrates In Muzzarelli R. A. A., Jeuniaux C., & Gooday G. W. (Eds.), Chitin in nature and technology (pp. 263–265). New York, NY: Plenum Press; 10.1007/978-1-4613-2167-5 [DOI] [Google Scholar]
- Beier, S. , & Bertilsson, S. (2011). Uncoupling of chitinase activity and uptake of hydrolyses products in freshwater bacterioplankton. Limnology and Oceanography, 56, 1179–1188. 10.4319/lo.2011.56.4.1179 [DOI] [Google Scholar]
- Beier, S. , Jones, C. M. , Mohit, V. , Hallin, S. , & Bertilsson, S. (2011). Global phylogeography of chitinase genes in aquatic metagenomes. Applied and Environment Microbiology, 77, 1101–1106. 10.1128/AEM.01481-10 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Beier, S. , Mohit, V. , Ettema, T. J. G. , Östman, Ö. , Tranvik, L. J. , & Bertilsson, S. (2012). Pronounced seasonal dynamics of freshwater chitinase genes and chitin processing. Environmental Microbiology, 14, 2467–2479. 10.1111/j.1462-2920.2012.02764.x [DOI] [PubMed] [Google Scholar]
- Benhabiles, M. S. , Salah, R. , Lounici, H. , Drouiche, N. , Goosen, M. F. A. , & Mameri, N. (2012). Antibacterial activity of chitin, chitosan and its oligomers prepared from shrimp shell waste. Food Hydrocolloids, 29, 48–56. 10.1016/j.foodhyd.2012.02.013 [DOI] [Google Scholar]
- Bishop, E. J. , Shilton, C. , Benedict, S. , Kong, F. , Gilbert, G. L. , & Gal, D. (2007). Necrotizing fasciitis in captive juvenile Crocodylus porosus caused by Streptococcus agalactiae: An outbreak and review of the animal and human literature. Epidemiology and Infection, 135, 1248–1255. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Bond, D. R. , Tsai, B. M. , & Russell, J. B. (1999). Physiological characterization of Streptococcus bovis mutants that can resist 2‐deoxyglucose‐induced lysis. Microbiology, 145, 2977–2985. 10.1099/00221287-145-10-2977 [DOI] [PubMed] [Google Scholar]
- Bowater, R. O. , Forbes‐Faulkner, J. , Anderson, I. G. , Condon, K. , Robinson, B. , & Kong, F. (2012). Natural outbreak of Streptococcus agalactiae (GBS) infection in wild giant Queensland grouper, Epinephelus lanceolatus (Bloch), and other wild fish in northern Queensland, Australia. Journal of Fish Diseases, 35, 173–186. 10.1111/j.1365-2761.2011.01332.x [DOI] [PubMed] [Google Scholar]
- Brochet, M. , Couve, E. , Zouine, M. , Vallaeys, T. , Rusniok, C. , & Lamy, M. C. (2006). Genomic diversity and evolution within the species Streptococcus agalactiae . Microbes and Infection, 8, 1227–1243. 10.1016/j.micinf.2005.11.010 [DOI] [PubMed] [Google Scholar]
- Busby, J. N. , Landsberg, M. J. , Simpson, R. M. , Jones, S. A. , Hankamer, B. , Hurst, M. R. H. , & Lott, J. S. (2012). Structural analysis of Chi1 chitinase from Yen‐Tc: The multisubunit insecticidal ABC toxin complex of Yersinia entomophaga . Journal of Molecular Biology, 415, 359–371. 10.1016/j.jmb.2011.11.018 [DOI] [PubMed] [Google Scholar]
- Chaiwarith, R. , Jullaket, W. , Bunchoo, M. , Nuntachit, N. , Sirisanthana, T. , & Supparatpinyo, K. (2011). Streptococcus agalactiae in adults at Chiang Mai University Hospital: A retrospective study. BMC Infectious Diseases, 11, 149–150. 10.1186/1471-2334-11-149 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Chernin, L. S. , Winson, M. K. , Thompson, J. M. , Haran, S. , Bycroft, B. W. , Chet, I. , … Stewart, G. S. A. B. (1998). Chitinolytic activity in Chromobacterium violaceum: Substrate analysis and regulation by quorum sensing. Journal of Bacteriology, 180, 4435–4441. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Choi, Y. J. , Kim, E. J. , Piao, Z. , Yun, Y. C. , & Shin, Y. C. (2004). Purification and characterization of chitosanase from Bacillus sp. strain KCTC 0377BP and its application for the production of chitosan oligosaccharides. Applied and Environment Microbiology, 70, 522–4531. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Chou, L. , Griffin, M. J. , Fraites, T. , Ware, C. , Ferguson, H. , Keirstead, N. , … Soto, E. (2014). Phenotypic and genotypic heterogeneity among Streptococcus iniae isolates recovered from cultured and wild fish in North America, Central America and Caribbean islands. Journal of Aquatic Animal Health, 26, 263–271. 10.1080/08997659.2014.945048 [DOI] [PubMed] [Google Scholar]
- Cottrell, M. T. , Moore, J. A. , & Kirchman, D. L. (1999). Chitinases from uncultured marine microorganisms. Applied and Environment Microbiology, 65, 2553–2557. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Dahiya, N. , Tewari, R. , & Hoondal, G. S. (2006). Biotechnological aspects of chitinolytic enzymes: A review. Applied Microbiology and Biotechnology, 71, 773–782. 10.1007/s00253-005-0183-7 [DOI] [PubMed] [Google Scholar]
- DeAngelis, K. M. , Lindow, S. E. , & Firestone, M. K. (2008). Bacterial quorum sensing and nitrogen cycling in rhizosphere soil. FEMS Microbiology Ecology, 66, 197–207. 10.1111/j.1574-6941.2008.00550.x [DOI] [PubMed] [Google Scholar]
- Delannoy, C. M. J. , Crumlish, M. , Fontaine, M. C. , Pollock, J. , Foster, G. , Dagleish, M. P. , … Zadoks, R. N. (2013). Human Streptococcus agalactiae strains in aquatic mammals and fish. BMC Microbiology, 13, 41 10.1186/1471-2180-13-41 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Eckert, E. M. , Baumgartner, M. , Huber, I. M. , & Pernthaler, J. (2013). Grazing resistant freshwater bacteria profit from chitin and cell‐wall‐derived organic carbon. Environmental Microbiology, 15, 2019–2030. 10.1111/1462-2920.12083 [DOI] [PubMed] [Google Scholar]
- Evans, J. J. , Bohnsack, J. F. , Klesius, P. H. , Whiting, A. A. , Garcia, J. C. , & Shoemaker, C. A. (2008). Phylogenetic relationships among Streptococcus agalactiae isolated from piscine, dolphin, bovine and human sources: A dolphin and piscine lineage associated with a fish epidemic in Kuwait is also associated with human neonatal infections in Japan. Journal of Medical Microbiology, 57, 1369–1376. 10.1099/jmm.0.47815-0 [DOI] [PubMed] [Google Scholar]
- Flach, J. , Pilet, P. E. , & Jolles, P. (1992). What's new in chitinase research? Experientia, 48, 701–716. 10.1007/BF02124285 [DOI] [PubMed] [Google Scholar]
- Gaffney, T. D. , Lam, S. T. , Ligon, J. , Gates, K. , Frazelle, A. , Di Maio, J. , … Allshouse, A. M. (1994). Global regulation of expression of antifungal factors by a Pseudomonas fluorescens biological control strain. Molecular Plant‐Microbe Interactions, 7, 455–463. 10.1094/MPMI-7-0455 [DOI] [PubMed] [Google Scholar]
- GIA (2010). Global Industry Analysis, MCP‐2039 p. 230.
- Gooday, G. W. (1990). The ecology of chitin degradation In Marshall K. C. (Ed.), Advance in microbiol ecology (Vol. 11, pp. 387–430). New York, NY: New Plenum Press; 10.1007/978-1-4684-7612-5 [DOI] [Google Scholar]
- Henrissat, B. , & Davies, G. (1997). Structural and sequence‐based classification of glycoside hydrolases. Current Opinion in Structural Biology, 7, 637–644. 10.1016/S0959-440X(97)80072-3 [DOI] [PubMed] [Google Scholar]
- Hirano, S. , & Nagao, N. (1989). Effects of chitosan, pectic acid, lysozyme, and chitinase on the growth of several phytopathogens. Agricultural and Biological Chemistry, 53, 3065–3066. [Google Scholar]
- Imoto, T. , & Yagishita, K. (1971). A simple activity measurement of lysozyme. Agricultural and Biological Chemistry, 35, 1154–1156. 10.1080/00021369.1971.10860050 [DOI] [Google Scholar]
- Jafar, Q. A. , Sameer, A. Z. , Salwa, A. M. , Samee, A. A. , Ahmed, A. M. , & Al‐Sharifi, F. (2008). Molecular investigation of Streptococcus agalactiae isolates from environmental samples and fish specimens during a massive fish kill in Kuwait Bay. Pakistan Journal of Biological Sciences, 11, 2500–2504. [DOI] [PubMed] [Google Scholar]
- Keirstead, N. D. , Brake, J. W. , Griffin, M. J. , Halliday‐Simmonds, I. , Thrall, M. A. , & Soto, E. (2014). Fatal septicemia caused by the zoonotic bacterium Streptococcus iniae during and outbreak in Caribbean reef fish. Veterinary Pathology, 51, 1035–1041. 10.1177/0300985813505876 [DOI] [PubMed] [Google Scholar]
- Keyhani, N. O. , & Roseman, S. (1997). Wild‐type Escherichia coli grows on the chitin disaccharide, N, N‐diacetylchitobiose, by expressing the cell operon. Proceedings of the National Academy of Sciences, 94, 14367–14371. 10.1073/pnas.94.26.14367 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Klesius, P. H. , Shoemaker, C. A. , & Evans, J. J. (2008). Streptococcus: A worldwide fish health problem. Proceedings of the 8th International Symposium on Tilapia in Aquaculture, Cairo, Egypt, pp. 83–107.
- Knorr, D. (1991). Recovery and utilization of chitin and chitosan in food processing waste management. Food Technology, 45, 114–122. [Google Scholar]
- Kong, M. , Chen, G. C. , Xing, K. , & Park, H. J. (2010). Antimicrobial properties of chitosan and mode of action: A state of the art review. International Journal of Food Microbiology, 144, 51–63. 10.1016/j.ijfoodmicro.2010.09.012 [DOI] [PubMed] [Google Scholar]
- Kurakake, M. , Yo‐u, S. , Nakagawa, K. , Sugihara, M. , & Komaki, T. (2000). Properties of chitosanase from Bacillus cereus S1. Current Microbiology, 40, 6–9. 10.1007/s002849910002 [DOI] [PubMed] [Google Scholar]
- Lee, H. W. , Choi, J. W. , Han, D. P. , Lee, N. W. , Park, S. L. , & Yi, D. H. (1996). Identification and production of constitutive chitosanase from Bacillus sp. HW‐002. Journal of Microbiology and Biotechnology, 6, 12–18. [Google Scholar]
- Liu, H. , Du, Y. , Wang, X. , & Sun, L. (2004). Chitosan kills bacteria through cell membrane damage. International Journal of Food Microbiology, 95, 147–155. 10.1016/j.ijfoodmicro.2004.01.022 [DOI] [PubMed] [Google Scholar]
- Liu, Y. L. , Jiang, S. , Ke, Z. M. , Wu, H. S. , Chi, C. W. , & Guo, Z. H. (2009). Recombinant expression of a chitosanase and its application in chitosan oligosaccharide production. Carbohydrate Research, 344, 815–819. 10.1016/j.carres.2009.01.027 [DOI] [PubMed] [Google Scholar]
- Manning, S. D. , Springman, A. C. , Lehotzky, E. , Lewis, M. A. , Whittam, T. S. , & Davies, H. D. (2009). Multilocus sequence types associated with neonatal group B streptococcal sepsis and meningitis in Canada. Journal of Clinical Microbiology, 47, 1143–1148. 10.1128/JCM.01424-08 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Mihara, S. (1961). Change in glucosamine content of Chlorella cells during the course of their life cycle. Plant and Cell Physiology, 2, 25–29. 10.1093/oxfordjournals.pcp.a077660 [DOI] [Google Scholar]
- Mobley, H. L. T. , Doyle, R. J. , Streips, U. N. , & Langemeier, S. O. (1982). Transport and incorporation of N‐acetyl‐D‐glucosamine in Bacillus subtilis . Journal of Bacteriology, 150, 8–15. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Murthy, N. K. S. , & Bleakley, B. H. (2012). Simplified method of preparing colloidal chitin used for screening of chitinase‐producing microorganisms. International Journal of Microbiology, 10, 1–5. [Google Scholar]
- Nedoma, J. , Vrba, J. , Hejzlar, J. , Šimek, K. , & Straškrabová, V. (1994). N‐acetylglucosamine dynamics in freshwater environments: Concentration of amino sugars, extracellular enzyme activities, and microbial uptake. Limnology and Oceanography, 39, 1088–1100. 10.4319/lo.1994.39.5.1088 [DOI] [Google Scholar]
- No, H. K. , Park, N. Y. , Lee, S. H. , & Meyers, S. P. (2002). Antibacterial activity of chitosans and chitosan oligomers with different molecular weights. International Journal of Food Microbiology, 74, 65–72. 10.1016/S0168-1605(01)00717-6 [DOI] [PubMed] [Google Scholar]
- Pelletier, A. , & Sygusch, J. (1990). Purification and characterization of three chitosanase activities from Bacillus megaterium P1. Applied and Environment Microbiology, 56, 844–848. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Phares, C. R. , Lynfield, R. , Farley, M. M. , Mohle‐Boetani, J. , Harrison, L. H. , & Petit, S. (2008). Epidemiology of invasive group B streptococcal disease in the United States, 1999‐2005. Journal of the American Medical Association, 299, 2056–2065. 10.1001/jama.299.17.2056 [DOI] [PubMed] [Google Scholar]
- Pochanavanich, P. , & Suntornsuk, W. (2002). Fungal chitosan production and its characterization. Letters in Applied Microbiology, 35, 17–21. 10.1046/j.1472-765X.2002.01118.x [DOI] [PubMed] [Google Scholar]
- Pruzzo, C. , Vezzulli, L. , & Colwell, R. R. (2008). Global impact of Vibrio cholerae interactions with chitin. Environmental Microbiology, 10, 1400–1410. 10.1111/j.1462-2920.2007.01559.x [DOI] [PubMed] [Google Scholar]
- Rabea, E. I. , Badawy, E.‐T. , Christian, V. , Stevens, C. V. , Smagghe, G. , & Steurbaut, W. (2003). Chitosan as antimicrobial agent: Applications and mode of action. Biomacromolecules, 4, 1457–1465. 10.1021/bm034130m [DOI] [PubMed] [Google Scholar]
- Rathore, A. S. , & Gupta, R. D. (2015). Chitinases from bacteria to human: Properties, applications, and future perspectives. Enzyme Research, 2015, 1–8. 10.1155/2015/791907 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Riemann, L. , & Azam, F. (2002). Widespread N‐acetyl‐Dglucosamine uptake among pelagic marine bacteria and its ecological implications. Applied and Environment Microbiology, 68, 5554–5562. 10.1128/AEM.68.11.5554-5562.2002 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Saito, J. , Kita, A. , Higuchi, Y. , Nagata, Y. , Ando, A. , & Miki, K. (1999). Crystal structure of chitosanase from Bacillus circulans MH‐K1 at 1.6‐A resolution and its substrate recognition mechanism. Journal of Biological Chemistry, 274, 30818–30825. 10.1074/jbc.274.43.30818 [DOI] [PubMed] [Google Scholar]
- Shapiro, J. A. (1998). Thinking about bacterial populations as multicellular organisms. Annual Review of Microbiology, 52, 81–104. 10.1146/annurev.micro.52.1.81 [DOI] [PubMed] [Google Scholar]
- Sheehan, B. , Labrie, L. , Lee, Y. S. , Wong, F. S. , Chan, J. , Komar, C. , … Grisez, L. (2009). Streptococcosis in tilapia; Vaccination effective against main strep species. Global Aquacult Advoc July/August, 72–74.
- Shimosaka, M. , Nogawa, M. , Wang, X. Y. , Kumehara, M. , & Okazaki, M. (1995). Production of two chitosanases from a chitosan‐assimilating bacterium, Acinetobacter sp. strain CHB101. Applied and Environment Microbiology, 61, 438–442. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Shoemaker, C. A. , Xu, D. H. , Garcia, J. C. , & LaFrentz, B. R. (2017). Capsular typing of Streptococcus agalactiae (Lancefield group B streptococci) from fish using multiplex PCR and serotyping. Bulletin of the European Association of Fish Pathologists, 37, 190–197. [Google Scholar]
- Shoemaker, C. A. , Xu, D. , & Soto, E. (2017). Streptococcus iniae and S. agalactiae In K Woo P. T., & Cipriano R. (Eds.), Fish viruses and bacteria: Pathobiology and protection (pp. 298–313). Boston, MA: CABI, Inc; 10.1079/9781780647784.0000 [DOI] [Google Scholar]
- Sørensen, U. B. , Poulsen, K. , Ghezzo, C. , Margarit, I. , & Kilian, M. (2010). Emergence and global dissemination of host‐specific Streptococcus agalactiae clones. mBio, 1, e00178‐10 10.1128/mBio.00178-10 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Sudarshan, N. R. , Hoover, D. G. , & Knorr, D. (1992). Antibacterial action of chitosan. Food Biotechnology, 6, 257–272. 10.1080/08905439209549838 [DOI] [Google Scholar]
- Uchida, Y. , Lzume, M. , & Ohtakara, A. (1989). Preparation of chitosan oligomers with purified chitosanase and its application In Skjak‐Brak G., Anthonsen T., & Sandford P. (Eds.), Chitin and chitosan: Sources, chemistry, biochemistry, physical properties and applications (pp. 373–382). London, UK: Elsevier. [Google Scholar]
- Vaaje‐Kolstad, G. , Horn, S. J. , Sørlie, M. , & Eijsink, G. H. (2013). The chitinolytic machinery of Serratia marcescenes – a model system for enzymatic degradation of recalcitrant polysaccharides. FEBS Journal, 280, 3028–3049. 10.1111/febs.12181 [DOI] [PubMed] [Google Scholar]
- Wei, X. L. , & Xia, W. S. (2003). Research development of chitooligosaccharides physiological activities. Chinese Pharmaceutical Bulletin, 19, 614–617. [Google Scholar]
- Xia, W. S. (2003). Physiological activities of chitosan and its application in functional foods. Journal of Chinese Institute of Food Science and Technology, 3, 77–81. [Google Scholar]
- Yang, T. C. , Chou, C. C. , & Li, C. F. (2005). Antibacterial activity of N‐alkylated disaccharidechitosan derivatives. International Journal of Food Microbiology, 97, 237–245. 10.1016/S0168-1605(03)00083-7 [DOI] [PubMed] [Google Scholar]
- Yildirim‐Aksoy, M. , & Beck, B. H. (2017). Antimicrobial activity of chitosan and a chitosan oligomer against bacterial pathogens of warmwater fish. Journal of Applied Microbiology, 122, 1570–1578. 10.1111/jam.13460 [DOI] [PubMed] [Google Scholar]
- Zakaria, M. B. , Zakaria, S. N. , Musa, M. , Hamilin, H. , & Zulkifly, N. A. H. (2012). Identification of chitosan‐degrading microbes for the production of chitooligomer. 3rd International Conference on Chemistry and Chemical Engineering IPCBEE, vol 38, IACSIT Press, Singapore.
- Zappulli, V. , Mazzariol, S. , Cavicchioli, L. , Petterino, C. , Bargelloni, L. , & Castagnaro, M. (2005). Fatal necrotizing fasciitis and myositis in a captive common bottlenose dolphin (Tursiops truncatus) associated with Streptococcus agalactiae . Journal of Veterinary Diagnostic Investigation, 17, 617–622. 10.1177/104063870501700620 [DOI] [PubMed] [Google Scholar]
- Zhang, D. , Bland, J. M. , Xu, D. , & Chung, S. (2015). Degradation of chitin and chitosan by a recombinant chitinase derived from a virulent Aeromonas hydrophila isolated from diseased channel catfish. Advances in Microbiology, 5, 611–619. 10.4236/aim.2015.59064 [DOI] [Google Scholar]
- Zhang, D. , Xu, D. , Qiu, J. , & Beck, J. (2017). Chitin degradation and utilization by virulent Aeromonas hydrophila strain ML10‐51K. Archives of Microbiology, 199, 573–579. 10.1007/s00203-016-1326-1 [DOI] [PubMed] [Google Scholar]
- Zheng, L. Y. , & Zhu, J. F. (2003). Study on antimicrobial activity of chitosan with different molecular weights. Carbohydrate Polymers, 54, 527–530. 10.1016/j.carbpol.2003.07.009 [DOI] [Google Scholar]
- Zhu, X. F. , Wu, X. Y. , & Dai, Y. (2003). Fermentation conditions and properties of a chitosanase from Acinetobacter sp. C‐17. Bioscience, Biotechnology, and Biochemistry, 67, 284–290. 10.1271/bbb.67.284 [DOI] [PubMed] [Google Scholar]
- Zhu, X. , Zhou, Y. , & Feng, J. (2007). Analysis of both chitinase and chitosanase produced by Sphingomonas sp. CJ‐5. Journal of Zhejiang University Science B, 8, 831–838. [DOI] [PMC free article] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Data Availability Statement
All data generated or analyzed during this study are included in this published article.
