Screening of alginate lyase-excreting microorganisms from the surface of brown algae
© The Author(s) 2017
Received: 13 January 2017
Accepted: 2 March 2017
Published: 4 April 2017
Alginate lyase is a biocatalyst that degrades alginate to produce oligosaccharides, which have many bioactive functions and could be used as renewable biofuels. Here we report a simple and sensitive plate assay for screening alginate lyase-excreting microorganisms from brown algae. Brown algae Laminaria japonica, Sargassum horneri and Sargassum siliquatrum were cultured in sterile water. Bacteria growing on the surface of seaweeds were identified and their capacity of excreting alginate lyase was analyzed. A total of 196 strains were recovered from the three different algae samples and 12 different bacterial strains were identified capable of excreting alginate lyases. Sequence analysis of the 16S rRNA gene revealed that these alginate lyase-excreting strains belong to eight genera: Paenibacillus (4/12), Bacillus (2/12), Leclercia (1/12), Isoptericola (1/12), Planomicrobium (1/12), Pseudomonas (1/12), Lysinibacillus (1/12) and Sphingomonas (1/12). Further analysis showed that the LJ-3 strain (Bacillus halosaccharovorans) had the highest enzyme activity. To our best knowledge, this is the first report regarding alginate lyase-excreting strains in Paenibacillus, Planomicrobium and Leclercia. We believe that our method used in this study is relatively easy and reliable for large-scale screening of alginate lyase-excreting microorganisms.
KeywordsAlginate lyase Gram’s iodine Alginate degradation Screening Brown algae
Alginate is an acidic linear polysaccharide found widely in cell walls of brown algae. It has been widely applied in food, cosmetic and pharmaceutical industries due to its unique physical properties to form gels (Wong et al. 2000). Alginate is composed of α-l-guluronic acid (G) and β-d-mannuronic acid (M) as structural units. Two kinds of hexuronic acid residues were linked by 1,4-O-glycoside bonds and can be degraded into alginate oligosaccharides (AOs) with low degree of polymerization by alginate lyases (Gacesa 1988; Ji 1997; Preiss and Ashwell 1962). As enzymatic degradation products of alginate, AOs are small and unsaturated alginate fragments with double bonds at the non-reducing end (Preiss and Ashwell 1962; Zhu and Yin 2015). These fragments with different structure and size exhibit various biological activities such as promotion of plant growth, anti-microbial, anti-oxidant, anti-tumor and immunomodulation (Falkeborg et al. 2014; Khan et al. 2012; Park et al. 2016; Saigusa et al. 2015; Wan et al. 1992; Xu et al. 2015; Yang et al. 2015; Zhou et al. 2015).
Alginate lyases are important and indispensable tools for production of AOs with special bioactivities (Wong et al. 2000; Zhu and Yin 2015). However, there are almost no commercialized alginate lyases with low cost and high yield until now. The narrow substrate specificity and low enzyme activity of existing enzymes still limit the industrial production of alginate oligosaccharides (Dou et al. 2013). Therefore, it is essential to continuously search and identify novel alginate lyases with high enzyme activity and wide substrate specificity from different sources. Nowadays, hundreds of alginate lyases have been isolated and identified from algae, marine mollusks and many kinds of microorganisms (Kawamoto et al. 2006; Matsubara et al. 2000; Zhu et al. 2015b, 2016a, b). Especially, different microorganisms have been reported to degrade alginate and become the most important sources of alginate lyases.
In order to acquire more alginate lyase-excreting microbes, a simple and efficient screening method needs to be developed. As an easy and convenient testing method, plate assay associated with constrain condition is traditionally used for bacteria screening. A number of alginate degrading strains were isolated by plate assay using different reagents as enzyme-producing indicator (e.g., cetyl pyridinium chloride, ruthenium red, calcium chloride, ethanol) (Gacesa and Wusteman 1990; Baron et al. 1994; Takeshita et al. 1991; Huang et al. 2013). Generally, a clear zone would occur around the alginate lyase-excreting colony after using the chromogenic agents. These qualitative methods make it possible to visualize the enzyme activity and can be applied to detect alginate lyase produced by bacterial colonies. However, the indistinct border and long reaction time of existing methods make the judgment of clear zones fairly difficult and inconvenient. The existing methods are still low efficient for revealing alginate lyase-excreting microbes at large scale. Recently, Sawant et al. (2015) reported that Gram’s iodine was an excellent chromogenic agent for revealing alginate lyase-producing colonies on agar plates. According Sawant’s result, Gram’s iodine could form distinct clear zones around the alginate degrading microbial colonies within 2–3 min. It was more effective than other chromogenic agents.
In this paper, we applied Gram’s iodine as chromogenic agent and a modified plate method with oxford cup to screening and compare alginate lyase-excreting microorganisms that are associated with the brown algae. Our goal is to screen novel alginate lyases at large-scales.
Materials and methods
Algae collection and bacteria isolation
Three kinds of brown algae Laminaria japonica (L. japonica), Sargassum horneri (S. horneri) and Sargassum siliquatrum (S. siliquatrum) were collected from the coast of Nanhuangcheng Island, China (38°21′N; 120°54′E), transferred to our laboratory and kept at 4 °C in a refrigerator. Each seaweed sample was cut into small pieces (2 cm × 2 cm). Ten grams of every sample were placed in a petri dish with 10 ml sterile water. The petri dishes were incubated at 30 °C until bacteria growing on the surface of seaweeds were easily observed with naked eyes (2–5 weeks). The bacteria were collected and diluted with sterile water. Aliquots (100 μl) of diluted sample were spread on screening plates consisted of 0.5% sodium alginate, 0.5% ammonium sulfate, 0.2% dipotassium phosphate, 0.1% magnesium sulfate, and 2% agar (ALG plates) (pH 7.2–7.4). The plates were incubated at 30 °C and checked daily until colonies were visible with naked eyes. Morphologically different colonies were numbered and transferred onto a new plate with the same medium. The new plate was incubated at 30 °C to form visible colonies, while the original plates were stained with Gram’s iodine solution (Sigma, St. Louis, USA, catalogue HT902). The clear zone around the strain colony indicated that the strain secreted alginate lyase into the medium (Sawant et al. 2015). The number of strains with clear zone was recorded and these strains were selected for further analysis.
Amplification, sequencing and phylogenetic analysis of the 16S rDNA
The genomic DNA of each strain was extracted by the EasyPure genomic DNA kit (Transgen Biotech, Beijing, China, catalogue #EE101-01). The 16S rRNA gene was amplified by PCR using primers 27F (5′-AGAGTTTGATCCTGGCTCAG-3′) and 1492R (5′-TACGGTTACCTTGTTACGACTT-3′). The enzyme was EasyPfu DNA polymerase (Transgen Biotech, Beijing, China, catalogue #AP211-01). The amplified DNA fragments were sequenced by Sangon Biotech Inc. (Shanghai, China). The sequencing data were analyzed using Basic Local Alignment Search Tool (BLAST 2.3.0) (https://blast.ncbi.nlm.nih.gov/Blast.cgi) and bacterial species were identified based on sequence identity from the database. Phylogenetic trees were constructed using neighbor-joining method and Kimura two parameter model in MEGA 5.1 program (Kumar et al. 2008).
Gram staining and microscopic observation
Fresh cells grown on ALG plate were picked up and spread on a microscope slide and stained with crystal violet (Beveridge 2001). The cells were observed with an optical microscope (Olympus BX51) using a 100× objective. Images were taken using an Olympus DP72 camera.
Alginate lyase activity assay
The identified strains were inoculated into 100 ml of liquid ALG medium (pH 7.0) and incubated at 30 °C for 24 h with constant agitation (200 rpm). The culture was centrifuged at 12,000 rpm for 5 min and the supernatant were collected. Protein concentrations of the supernatants were detected using a protein quantitative kit (TransGen Biotech, Beijing, China).The enzyme activity was measured by two different methods:
Gram’s iodine method
200 μl of supernatant were added into an oxford cup and was placed on the surface of the ALG plate. The plates were incubated at 30 °C for 24 h and then stained with Gram’s iodine solution. The inner and outer diameters of the cleared zone were measured and the total area of the cleared zone was calculated. One unit of enzyme activity was defined as the amount of enzyme required to increase the cleared zone area by 0.1 mm2/min.
Ultraviolet absorption method
200 μl of supernatant were mixed with 1.8 ml liquid ALG medium. The mixtures were incubated at 30 °C for 24 h. The mixtures were heated to 100 °C for 10 min to stop the reaction. Absorbance at 235 nm was measured to determine the enzyme activity. One unit of enzyme activity was defined as the amount of enzyme required to increase 0.1 of the absorbance value at 235 nm/min (Preiss and Ashwell 1962).
Determination of optimum conditions for producing alginate lyase
Effects of temperature, pH and alginate concentration on alginate lyase activity were tested using the selected enzyme-excreting strains. The strain incubated in 100 ml of ALG medium at 30 °C, 200 rpm for 24 h at various temperature, pH, time intervals and alginate sodium concentrations. The effect of temperature on alginate lyase activity was determined at temperature ranging from 20 to 40 °C. The pH effect was determined at pH ranging from 5 to 9 at an interval of 1-pH unit. The effect of alginate sodium concentrations was determined at the concentrations ranging from 0 to 1.2% at an interval of 0.2% unit. The effect of fermentation time was determined at time ranging from 0 to 24 h at an interval of 4 h. Unless otherwise specified, all fermentations were performed at 30 °C and pH 7.0. Alginate lyase activity was measured as described above.
Detection of degradation product of alginate lyase
Thin layer chromatography (TLC) was applied to analyze alginate oligosaccharides produced by novel alginate lyase-exerting stains. TLC was performed according to the method described by Huang et al. (2013) and the loading volume was 2 μl. Fermentation samples at different time were collected and spotted on a TLC plate (Merck, Germany) with 1-butanol/formic acid/water (4:6:1 v:v:v) as a mobile solvent. Then the plate was sprayed with 10% (v/v) sulfuric acid in ethanol and heated at 110 °C for 10 min.
The fermentation broth of LJ-3 with AOs was collected and precipitated by adding ethanol (3 volumes) to remove higher molecular weight components. The solution was centrifuged at 12,000 rpm centrifuging for 15 min, then the supernatant was freeze-drying and then re-dissolved in deionized water. ESI–MS analysis was performed using a LCQ Fleet mass spectrometer (Thermo Fisher Scientific, USA) in negative mode.
Sequences accession and strain deposition
16S rRNA gene sequences of identified alginate lyase-excreting strains were submitted and available in the GenBank Database under the Accession Number KX959962–KX959973. The deposition number of LJ-3 was CGMCC 12,155.
Identification of alginate lyase-excreting bacteria
Identified isolates, each with the closest type strain, the 16S rRNA gene similarity and the observed enzyme activities
Closest bacterial strain (EZTaxon)
Diameter of clearance zone (cm)
2.3 ± 0.2
0.8 ± 0.1
1.4 ± 0.2
1.7 ± 0.2
1.7 ± 0.2
1.2 ± 0.1
1.6 ± 0.2
1.4 ± 0.1
1.1 ± 0.1
0.8 ± 0.1
1.1 ± 0.1
1.5 ± 0.2
Evaluation of alginate lyase activities
Optimization of growth conditions for production of alginate lyase secreted by LJ-3 strain
Product analysis of alginate lyase-excreting strains
In fermentation broth of LJ-23 and SS-92 strains, AOs were also first detected at 8 h but the amount and DPs were maximized during 12–16 h. AOs were first detected at 16 h in fermentation broth of LJ-22 strain and only oligomers of DP2 and DP3 were detected. This result indicated that the alginate lyases of the five stains had different endolytic reaction mode. Thus, these alginate lyases could be useful tools for the preparation of alginate oligosaccharides with different DPs.
No AOs in fermentation broth of LJ-16 and SH-45 were detected. We inferred that the enzyme activities of LJ-16 and SH-45 strains were too low to produce enough oligosaccharides for detection by TLC or the consumption of oligosaccharides by strains was too fast to detect at 4-h sampling interval.
Bacteria screening is generally time consuming and labor-intensive. In our study, we applied Gram’s iodine method to isolate alginate lyase-excreting microorganism and confirmed that it was practical and convenient. The screening procedure was shown in Additional file 2: Figure S2. In combination with oxford cup method, we modified the Gram’s iodine method to achieve quantitative analysis of alginate lyase activity on a single plate. The quantification is validated with ultraviolet absorption method. The Gram’s iodine method requires no special equipment, making it suitable for large-scale screening and comparing of alginate lyase-excreting microorganism.
In the past several years, numerous alginate lyases have been isolated from different microorganisms, especially from those associated with brown algae. For example, 21 alginate lyase-excreting strains were isolated from the surface of the Arctic Laminaria and some cold-adapted alginate lyases were identified (Dong et al. 2012). More recently, Martin et al. (2015) isolated and identified 14 alginate lyase-excreting strains associated with the brown alga Ascophyllum nodosum, including one novel strain of Marinomonas. In this study, we identified 12 alginate lyase-excreting strains from the surfaces of three brown algae. Among them, novel alginolytic activity in Paenibacillus, Leclercia and Planomicrobium has not been previously reported. Paenibacillus produces many kinds of extracellular enzymes such as cellulose, proteases, amylase and other polysaccharide-degrading enzymes, which can be used in a wide range of industrial fields (Adlakha et al. 2015; Budi et al. 2000; Das et al. 2016; Dong et al. 2016; Lan Pham et al. 1998; Mathews et al. 2016). However, production of alginate lyase by Paenibacillus has never been reported. In this study, 4 alginate lyase-excreting strains belonging to Paenibacillus (LJ-22, LJ-23, LJ-32 and SS-92) were isolated from two different algae (L. japonica and S. siliquatrum). As shown in Additional file 3: Table S1, three of them (LJ-23, LJ-32 and SS-92) showed high enzyme activities compared to enzyme activities published previously (Li et al. 2015; Zhu et al. 2015a, b; 2016a). Our results indicated that Paenibacillus is a potential source for novel alginate lyase.
Although alginate lyases from the genus Bacillus were found in a few reports (Nakagawa et al. 1998), they may play an important role in aquaculture and agriculture. Recently, an alginate-degrading Bacillus strain was applied to improve the seaweed (L. japonica) based diet for sea cucumber (Apostichopus japonicas) (Wang et al. 2015). An alginate lyase-excreting strain (LJ-3) belonging to Bacillus genus was isolated in our study and it has potential to be used in industry due to its high enzyme activity. It could also be used as plant stimulant in agriculture. We showed that alginate oligosaccharides produced by LJ-3 strain could improve growth and quality of plants (unpublished data), especially promote early fruit coloring (Additional file 4: Figure S3).
degrees of polymerization
WMP and CL designed the work, performed the research study and drafted the manuscript. ZZJ was involved in critically revision the manuscript. WXJ guided and participated in collection of algae samples. QS and YPS designed and supervised the research study. All authors read and approved the final manuscript.
The authors declare that they have no competing interests.
Availability of data and materials
This work was supported by the National Key Technology R&D Program of China (2013BAB01B0), the Young Scientists Fund of National Natural Science Foundation of China (41401285), the Public Science and Technology Research Funds Projects of Ocean (201505022), the Chinese Academy of Sciences Strategic Pilot Project (XDA1102040300) and Shandong Science and Technology Development Project (2010GSF10208).
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