Antimicrobial Activity of Heterotrophic Bacterial Strains of Marine Origin

authors:

avatar Beleneva Irina Alekseevna 1 , avatar Kukhlevsky Andrey Danilovich 2 , 3 , avatar Kharchenko Ulyana Valerievna 3 , *

A.V. Zhirmunsky Institute of Marine Biology, Far East Branch, Russian Academy of Sciences, Vladivostok, Russia
Far-Eastern Federal University, Vladivostok, Russia
Institute of Chemistry Far Eastern Branch of Russian Academy of Science, Vladivostok, Russia

how to cite: Irina Alekseevna B, Andrey Danilovich K, Ulyana Valerievna K. Antimicrobial Activity of Heterotrophic Bacterial Strains of Marine Origin. Jundishapur J Microbiol. 2013;6(2): 166-175. https://doi.org/10.5812/jjm.5039.

Abstract

Background:

Bacterium-bacterium antagonistic interactions could be important in the ecology of marine bacteria. Antimicrobial properties of microorganisms are exploited in various fields of human activities.

Objectives:

Antagonism of heterotrophic bacteria from different marine environments of tropical and temperate zones was examined.

Materials and Methods:

Bacteria were isolated from biofilm samples, tissues of hydrobionts and sea water. Isolates were characterized by phenotypic and 16S rRNA phylogenetic analyses. Agar diffusion assay was applied to investigate inhibitory interactions. 5 type strains and 21 strains of marine origin were used as test cultures.

Results:

68.97% of isolates from temperate zone and 56.76% of tropical zone showed antimicrobial activity. The most active strains belonged to genera Pseudomonas and Pseudoalteromonas.

Conclusions:

Bacterial interspecies growth inhibition is widely distributed in marine environments. Marine bacteria, especially Vibrio spp., may be good probiotics which are active against pathogenic bacteria.

1. Background

Bacterium-bacterium interactions, diverse in form and content are widely seen in water column with different microparticles. Over one half of marine bacteria examined so far have displayed antagonistic activity towards other pelagic bacteria. Antimicrobial interactions influence, first, the structure of the microbial community and second, the functioning of microbial cenoses (1). Microbial antagonism results from the effects of antibiotic substances inhibiting the growth of microorganisms or killing them. Bacterial production of secondary metabolites, in particular growth inhibitors, is one of the adaptation mechanisms, which gives advantage in competition for available nutrients and living space.

Searching for previously unknown microbial strains is an effective approach to obtain new biologically active substances. Marine bacteria are producers of unique substances which have never been found in terrestrial organisms (2, 3). Secondary metabolites of microbial origin are widely used in various fields of human activities, such as medicine, agriculture, pharmaceuticals, food processing, chemical industries and many others. In addition to production of antibiotics and lytic enzymes (4), the antimicrobial properties of microorganisms are used to work out biofilms with anticorrosion and antifouling properties (5, 6) and to enhance crop protection against phytopathogenic bacteria (7) and fungi (8).

In aquaculture, the usage of live cultures of antagonistic bacteria as probiotics is developing to prevent outbreaks of diseases in aquatic organisms (9, 10). The interest to biological control in the past two decades has increased dramatically due to expanding opportunities for synthesis of biological products and highly competitive chemical preparations which could often inflict enormous damage to the environment (11).

2. Objectives

The aim of our study was to investigate the peculiarities of bacterium-bacterium antagonistic interactions among heterotrophic bacteria of marine origin in tropical and temperate zones. This would be helpful to clarify some problems concerning the role of biosynthesis of antimicrobial substances in natural bacterial communities and could also be helpful to develop a strategy of search for new physiologically active substances of bacterial origin.

3. Materials and Methods

3.1. Sampling

Heterotrophic bacteria were isolated from different marine objects in Nha Trang Bay, South China Sea in June–July 2008 and January 2009; in the pelagic part of the East China Sea in April 2010; and in Peter the Great Bay, Sea of Japan, in August 2008, 2009 and 2010 in Nha Trang Bay. Invertebrates and algae were collected by scuba divers from depths of three to 23 meters. Microflora samples of the fouling of copper-containing and aluminum plates were selected on a test bench of Marine Corrosion Station, Primorsky Branch of Russian-Vietnamese Tropical Center, Nha Trang (Vietnam). Water samples were taken directly at exposure points of metal plates. The samples of algae included the green alga Caulerpa lentillifera and brown algae Padina spp., Turbullaria spp. and Sargassum spp. The samples of animals included the ascidian Didemnum molle, bivalves Pinctada margaritifera and Crassostrea gigas and unidentified species of sponges (three samples).

3.1.1. Open Part of the East China Sea

Water samples were collected using a Niskin bottle at the points with coordinates 29 º 40, 647 'N, 124 º 27, 909 'E and 26 º 46, 326 'N, 121º 41, 916 'E.

3.1.2. Peter the Great Bay

The samples of algae, animals and water were collected by scuba divers in Avangard Bight of Peter the Great Bay. The examined animals included bivalves Crenomytilus grayanus, Modiolus dificillus and C. gigas; echinoderms, sea urchins Strongylocentrotus nudus and S. intermedius; starfishes Patiria pectinifera and Asterias amurensis, and sea cucumber Apostichopus japonicus and the ascidian Halocynthia aurantium. The seaweed Laminaria japonica was examined from the plants. As test cultures the following type strains were applied: Escherichia coli ATCC 15034, Bacillus subtilis BKM B501, Candida albicans KMM 455, Pseudomonas aeruginosa KMM 433 and Staphylococcus aureus ATCC 21027.

3.2. Isolation of Bacteria in Pure Cultures and Phenotypic Characterization of the Isolates

Isolation of bacteria from hydrobionts and seawater and preservation of bacterial strains were conducted as described elsewhere (12). Bacteria were isolated from internal tissues of ascidians and sponges, coelomic fluid and digestive tract of sea urchins, bivalves and starfishes and digestive tract of holothurians. Biofilm samples (8 cm2 in area) were scrapped off from the surface of each metal plate using a stencil and a sterile tool and then carefully taken with a sterile absorbent cotton stick. The stick with the microbial mass was placed into a test tube containing 2 ml of sterile seawater.

Serial dilutions of homogenates, biofilm suspensions and water samples (0.1 ml) were plated on solid Youschimizu–Kimura medium (13) with the following composition: peptone (5.0 g), yeast extract (2.0 g), glucose (1.0 g), К2НРО4 (0.2 g), MgSO4•7H2O (0.1 g), agar (12.0 g), distilled water (500 ml), and seawater (500 ml); the рН of the medium equaled 7.8 to 8.0. Cetrimide agar (Serva) supplemented with glycerol in proportion of 10 g/l was used to isolate bacteria of the genus Pseudomonas. The plates were incubated for three to ten days at 28 °С for tropical isolates and at 23 °С for isolates from temperate zone.E. coli, C. albicans, S. aureus, P. aeruginosa and B. subtilis were cultured on tryptic soya agar (TSA, Difco).

Motility and cell morphology were observed by the hanging-drop method. Gram-reaction, oxidase and catalase activities, presence of nitrate reductase, sodium ion requirements and tolerance to different NaCl concentrations (0–12% NaCl), growth at different temperatures (4–42 °C), acid production from sugars, production of lysine and ornithine decarboxylases and arginine dehydrolase and gelatinase, DNA base composition and resistance to antibiotics were tested as described elsewhere (14). The following antibiotics were used for tests: ampicillin (Amp), erythromycin (Ery), gentamicin (Gen), lincomycin (Lin), rifampicin (Rif), oleandomycin (Ol), polymyxin B (Pol) and vibriostatic agent O-129 (2,4-diamino-6,7-di-isopropylpteridine) with Oxoid disks. Additional biochemical tests with API-20NE and API-20E test kits (bioMérieux) were performed as described by the manufacturers, except that strains were suspended in 3% NaCl.

3.3. 16S rRNA Gene Sequence Analysis of Bacterial Isolates

Total DNA was isolated using the standard technique (15). A fragment of 16S rRNA gene sequence was amplified in 25 µl of reaction mixture comprising 2.5 µl of 10 × PCR buffer, 2 µl of 10 mM dNTP mixture (2.5 mM each), 2.5 µl of each primer (2.5 μM), 10 ng of DNA and 1 unit of Taq DNA polymerase (Fermentas). Primers amplification were performed according to Lane (16). The PCR amplification (GeneAmp PCR System 9700, Applied Biosystems) was performed using the following scheme: an initialization hold at 95 °C for three minutes, 35 cycles each comprising 30 seconds at 94 °C, one minute at 56 °C and 1.5 minutes at 72 °C and the final hold at 72 °C for five minutes.

The purity and size of products were estimated in 1% agarose gel. The purified amplification products were applied as a matrix for sequencing, which was performed with a BigDye Terminator v3.1 Cycle Sequencing Kit (Applied Biosystems). The purified products of sequencing were subjected to electrophoresis with an ABI Prism 3130 genetic analyzer, on a 50 cm capillary cartridge. The obtained direct and inverse sequences for each tested species were aligned using SeqScape v2.6 (Applied Biosystems) software. The obtained fragments of 16S rRNA gene sequences were deposited in NCBI/GenBank (GenBank accession numbers. GU579451, GU579452, GU726840–GU726880, JN679843–JN679865). Phylogenetic trees were developed with the Neighbor-Joining Method (NJ) (17), using Kimura's two-parametric model of nucleotide substitutions (K2P) (18) and MEGA 5 software (19). Cluster stability was estimated using bootstrap analysis (1000 iterations) (20).

3.4. Screening of Isolates for Inhibitory Interactions

Antimicrobial activity was tested in strains isolated in Vietnam from the surface of metal plates fouling and seawater and in Russian isolates associated either with different hydrobionts or with free-living in seawater. As test cultures strains were used isolates in tropical and temperate zones from seawater and different hydrobionts and five type strains belonging to Gram-positive bacteria, Gram-negative bacteria and yeasts. Antimicrobial activity of the isolates was assayed with a slightly modified method of Long and Azam (1). A lawn of a target isolate was prepared by mixing 25 ml of molten (44 °C), 0.6% Marine agar with 0.5 ml of isolate suspension. The suspension was prepared by dilution of an MA-grown daily culture in physiological solution down to concentration of 109 cells/ml, according to the McFarland Turbidity Standard. From 12 to 16 strains of potential growth inhibitors were spotted on the lawn. The plates were incubated face up for six days at 28 °С for tropical isolates and at 23 °С for temperate zone and examined daily for zones of inhibition. Potential producers were considered positive, if the diameter of the inhibition zone was at least 4 mm greater than that of the colony formed by the potential producer.

4. Results

4.1. Identification of Bacteria

Among 66 strains analyzed for antimicrobial activity, 61 strains were identified using results of 16S rRNA gene sequencing ( Figure ).

Strains Isolated from Peter the Great Bay, Sea of Japan, Russia and Nha Trang Bay, South China Sea, Vietnam Are Shown in Blue and Black, Respectively.
Strains Isolated from Peter the Great Bay, Sea of Japan, Russia and Nha Trang Bay, South China Sea, Vietnam Are Shown in Blue and Black, Respectively.

The strains used as test cultures and five antagonistic strains were identified by phenotypic characteristics. The obtained data was compared with available literature to corroborate the identification of some bacterial strains. To specify the taxonomic position of some strains, antibiotics sensitivity test was applied. For example, the strain 1541 Pseudoalteromonas sp, tested for antimicrobial activity, showed oxidative metabolism pattern, possessed cytochrome oxidase, demonstrated low G/C DNA molar percentage ratio (39.5%) and had dark brown pigment which diffused into the medium; it hydrolyzed agar and did not possess nitrate reductase. It was sensitive to rifampicin, ampicillin, erythromycin, gentamicin and polymyxin, but resistant to lincomycin and oleandomycin.

Proceeding from phylogenetic and phenotypic analysis the strains examined for antimicrobial activity were divided into five different phylogenetic groups as follow: γ- Proteobacteria (66.7%), Firmicutes (27.3%), α-Proteobacteria (3%), Actinobacteria (1.5%), and Bacteroidetes (1.5%). Most of γ-Proteobacteria belonged to genera Pseudomonas and Pseudoalteromonas; bacteria of genera Vibrio, Shewanella, Alteromonas, Enterobacter, and Stenotrophomonas were registered as minor groups ( Table 1 ). Firmicutes mostly constituted of species of the genus Bacillus and also included significantly fewer members of genera Staphylococcus and Planococcus.

The group of α-Proteobacteria included genera Ruegeria and Paracoccus; while phyla Bacteroidetes and Actinobacteria included one registered member each, namely the genera Sphingobacterium and Brevibacterium, respectively. Most Russian isolates obtained from different hydrobionts were categorized as γ- Proteobacteria, whereas more than a half of tropical isolates from the surface of copper-containing plates belonged to Firmicutes. Most of 21 strains identified by phenotypic characteristics belonged to genera Bacillus and Vibrio ( Table 2 ). Genera Xanthomonas, Enterobacter, Planococcus and Serratia included one registered species each. The taxonomic position of strains 1335 and 1336 (S. oneidensis) and the strain 1355 (P. fluorescens), which were examined for capability to produce antimicrobial compounds and also were used as test cultures was determined using the results of 16S rRNA gene sequencing.

Table 1

Sources and Taxonomic Position of Bacterial Strains Tested for Antimicrobial Activity

Strain No./ Gene Bank Ref. No. Source of Isolation Close Phylogenetic Relatives Identity, %
Vietnam, Nha Trang Bay, South China Sea      
1242/GU726840 a brass P 100
1248/GU726841brassP. aeruginosa 100
1263/GU726843 bronze Alteromonas sp. 100
1341/GU726850 brass B 100
1343/GU726852 brass Bacillus sp. 99,6
1344/GU726853 brass P 96,6
1345/GU726854 brass B 100
1346/GU726855 brass B 100
1347/GU726856 brass S 100
1348/GU726857 brass B 100
1349/GU726858 brass B 99,8
1350/GU726859 bronze P 97,3
1351/GU726860 bronze Alteromonas sp. 99.9
1352/GU726861 bronze B 100
1353/GU726862 bronze Alteromonas sp. 99,9
1355/GU726863 copper P 100
1360/GU726864 copper Enterobacter sp. 99,5
1361/GU726865 copper B 100
1364/GU726866 copper Brevibacterium sp. 99,9
1365/GU726867 copper B 100
1366/GU726868 copper B 99,9
1367/GU726869 brass B 100
1368/GU726870 brass B 100
1369/GU726871 brass B 100
1373/GU726872 brass P 99,9
1374/GU726873 seawater V 99,6
1382/GU726874 aluminum Stenotrophomonas sp 100
1389/ aluminum P 100
1391/GU726876 copper Paracoccus sp. 99,1
1392/GU726877 brass Sphingobacterium sp. 99,3
1405/GU726879 sponge B 99,9
1441 seawater Staphylococcus sp. n/d b
1442 seawater Staphylococcus sp. n/d
1443 seawater Vibrio sp. n/d
Vietnam, Nha Trang Bay, South China Sea; The East China Sea      
1444 seawater Ruegeria sp.99,9
1541 seawater Pn/d
1542 seawater Vibrio sp.n/d
Peter the Great Bay, Japan Sea, Russia      
915/EU579451 trepang V99.8
929 trepang V99.1
1298/GU726844 sea urchin V99,9
1306/GU726845 laminaria V99,9
1314/GU726846 soil P100
1333 ouster P99,6
1335/GU726848 ouster S99,8
1336/GU726849 ouster S99,8
1561 seawater P 99,5
1562 seawater P 99,5
1567 starfish P 99.9
1569/JN679848 starfish P 99.9
1570 sea urchin P 99.9
1573 starfish P 97.3
1576 starfish P 100
1579 bivalve P 99.2
1582 starfish P 99.6
1589 starfish P 99.9
1593 starfish P 99.9
1594 sea urchin P 99.9
1595 trepang P 97.1
1596 bivalve P 99.9
1597 holothurian P 99.9
1599 bivalve P 99,9
1601 bivalve P 99.8
1602 sea urchin P 99.9
1603 sea urchin P 99.9
1604 sea urchin P 99.9
1605 sea urchin P 99.9
Table 2

Sources and Taxonomic Position of Bacterial Test-Culture Strains

Strain No. Source of Strain Close Phylogenetic Relative Identity, %
1420 Vietnam, holothurian Bacillus n/d
1421 Vietnam, holothurian Bacillus n/d
1422 Vietnam, holothurian Bacillus n/d
1423 Vietnam, holothurian Vibrio n/d
1424 Vietnam, holothurian Vibrio n/d
1425 Vietnam, holothurian Vibrio n/d
1427 Vietnam, ouster Vibrio n/d
1430 Vietnam, algae Bacillus n/d
1437 Vietnam, algae Bacillus n/d
1438 Vietnam, algae Bacillus n/d
1478 Vietnam, seawater Bacillus n/d
1537 Vietnam, seawater Vibrio n/d
1543 Vietnam, seawater Xanthomonas n/d
1306 / GU726845 Russia, laminaria V 99.9
1331 Russia, trepang Enterobacter sp. n/d
1333 / GU726847 Russia, ouster P 99.6
1335 Russia, ouster S 99.8
1336 Russia, ouster S 99.8
1355 Vietnam, copper P 100
1410 Vietnam, aluminum S99.9
1530 Vietnam, bivalve Vibrio sp. n/d
ATCC 15034 КММ, PIBOC* E n/d
КММ 455 КММ, PIBOC C n/d
ATCC 21027 КММ, PIBOC S n/d
B КММ, PIBOC B n/d
КММ 4 КММ, PIBOC P n/d

4.2. Antimicrobial Activity

68.97% of isolates from temperate zone and 56.76% of Vietnamese strains showed antimicrobial activity. The strains that showed the greatest activity were of tropical origin ( Table 3 ). Regarding taxonomic position of the most active strains, in both temperate and tropical zones, the undisputed leaders belonged to families Pseudomonadaceae and Pseudoalteromonadaceae (Table 3 and Table 4). Among Vietnamese isolates the activity against most test cultures, besides P. aeruginosa and P. nigrifaciens, was also demonstrated by Ruegeria sp. and Bacillus spp.

All tropical strains of Alteromonas spp., Pseudomonas spp., Pseudoalteromonas spp. and Vibrio spp. tested for antimicrobial activity appeared active against two or more test cultures. 35.7% of the genus Bacillus members showed antimicrobial activity . Two strains of Russian origin, P. putida no. 1567 and no. 1602, suppressed growth in 10 and 11 test cultures respectively (Table 4). Among pseudomonads 71.4% of strains demonstrated antimicrobial activity. A strain of P. piscicida suppressed growth in 10 test cultures. All Vibrio strains showed antimicrobial activity in respect to 1–4 test cultures. No antimicrobial activity was detected in the examined strains of S. oneidensis and P. maritimus and certain strains of Pseudomonas spp.

Vietnamese isolates were the most active against bacteria of genera Bacillus and Vibrio; Russian strains showed the greatest activity against Bacillus spp., S. marcescens, S. oneidensis and Vibrio spp. Tropical isolates suppressed more actively the growth of E. coli and S. aureus, whereas strains from temperate area were more active against P. aeruginosa. None of Russian isolates showed activity against P. fluorescens and C. albicans, whereas tropical strains of P. citrea and Ruegeria sp. suppressed the growth of P. fluorescens, while P. nigrifaciens and Alteromonas sp. were active against C. albicans.

Table 3

Antagonistic Activity of Bacterial Isolates From Nha Trang Bay, South China Sea, Vietnam

  1420 1421 1422 1423 1424 1425 1427 1430 1437 1438 1478 1537 1543
1242 + a + + + - + + + + - + + +
1248 + + + + + + + + - - + + +
1263 - b - - - - - + - - - - - -
1343 - - - - - - - - - - - - -
1344 + + + + - - - + - - + - -
1348 + - - - - - + - - - - - -
1349 - + - - - - + - - - - - -
1350 + - - + - + - + + - + - -
1351 - - - - - - + - - - - + -
1353 + - - + - - - + - - - - -
1355 - - - - - - - + + - - - -
1361 + - + - - + - - - - - - +
1366 - - - - - - + - - - + + -
1373 - - - - + - - + - - - - +
1374 - - - - - - + - - - + - -
1389 + - - + - - - - - - + - -
1442 - - - - - - - - - + - - -
1443 + + - - + - - - - - - - -
1444 + + + + - - + - + + + - -
1541 - + - + - - - + + - - - -
1542 - - - - - - - + - + - - -
 E. coliC. albicansS. aureusP. aeruginosaB.subtilis13061331133313351336135514101530
1242 - - + - + + + - + + - + +
1248 - - + - + + + - + - - + +
1263 - - - - - + - - - - - - +
1343 + - - - - - + - - - - - -
1344 - + - + - - - - - - - - -
1348 + - - - + - - - - - - - -
1349 - - + - - - + - - - - + -
1350 - - + - - - - + - - - - -
1351 - - - - - + - - - - - - -
1353 - + - - - - - - - - - - -
1355 + - - - + - + - - - n/d c + +
1361 + - + - - - - - - - - - -
1366 + - - - - + - - + - - - +
1373 - - - - - - - - - + + - +
1374 - - - - - - - - - - - - +
1389 + - - - - - - - - - - + -
1442 - - - - - - - - - - - - -
1443 - - - - - - - - - - - - -
1444 + - + - - - - + + + + - -
1541 - - - - - - - - + + - - -
1542 - - - - - - - - - - - - -
Table 4

Antagonistic Activity of Bacterial Isolates From Peter the Great Bay, Sea of Japan, Russia

  1420 1421 1422 1423 1424 1425 1427 1430 1437 1438 1478 1537 1543
915 - - - - - - + - - - - - -
929 - - - + - + - - - - - + -
1298 - - - - - - + - - - - + -
1306 - - - - - - - - - - - + -
1314 - - - + - - + - - - + + -
1561 - - - - - + - - - - - + -
1562 - - - - - - - - - - - - -
1567 + + + + - - - + - + + - -
1569 - + + - - + - + + + - - +
1570 - - - - - - - + + - - + -
1576 - + - - - - - - - - - - +
1579 - + - - - - - - - - + - -
1582 + + - - - - - - - - - - -
1594 + + + - - - - + + + - - -
1596 - + - - + - - + - - - - -
1597 - - - - - - - - - - - - +
1602 + + + - + - - + + + - - -
1603 - + + - + - - + - - - - -
1604 - + + - + - - + - + - - -
1605 + - + - + - - + - - - - -
915 - - - - - - - - - - - - -
929 - - - - - + - - - - - - -
1298 - - - - - + - - - - - - +
1306 - - - - - n/d - - - - - - -
1314 + - + - - - + - + - - + +
1561 - - - - + + + - + - - + +
1562 - - + - + + + + - - - + -
1567 - - - - + + - + - - - - -
1569 - - - - - + + + - - - - -
1570 - - - - - + - - + + - + +
1576 - - - - - - - - - - - - -
1579 - - - - - - - - - - - - -
1582 - - - - - - - - - - - - -
1594 - - - - - - - - + - - - -
1596 - - - - - - - - + - - + -
1597 - - - - - - - - - - - - -
1602 - - - + - - - - + + - + -
1603 - - - + - - - - + + - - -
1604 - - - + - - - - + - - - -
1605 - - - + - - - - - + - - -

Acknowledgements

References

  • 1.

    Long RA, Azam F. Antagonistic interactions among marine pelagic bacteria. Appl Environ Microbiol. 2001;67(11):4975-83. [PubMed ID: 11679315]. https://doi.org/10.1128/AEM.67.11.4975-4983.2001.

  • 2.

    Fenical W, Jensen P. Marine Biotechnology. New York: Plenum Press. 1993. p. 419-57.

  • 3.

    Wagner-Dobler I, Beil W, Lang S, Meiners M, Laatsch H. Integrated approach to explore the potential of marine microorganisms for the production of bioactive metabolites. Adv Biochem Eng Biotechnol. 2002;74:207-38. [PubMed ID: 11991180]. https://doi.org/10.1007/3-540-45736-4_10.

  • 4.

    Leifert C, Li H, Chidburee S, Hampson S, Workman S, Sigee D, et al. Antibiotic production and biocontrol activity by Bacillus subtilis CL27 and Bacillus pumilus CL45. J Appl Bacteriol. 1995;78(2):97-108. [PubMed ID: 7698955]. https://doi.org/10.1111/j.1365-2672.1995.tb02829.x.

  • 5.

    Akid R, Wang H, Gobata M, Smith T, Gittens J. Green coatings for industrial applications. Corrosion management. 2011;100:11-4.

  • 6.

    Burgess JG, Boyd KG, Armstrong E, Jiang Z, Yan L, Berggren M, et al. The development of a marine natural product-based antifouling paint. Biofouling. 2003;19 1:197-205. [PubMed ID: 14618721]. https://doi.org/10.1080/0892701031000061778.

  • 7.

    Montealegre JR, Reyes R, Pérez LM, Herrera R, Silva P, Besoain X. Selection of bioantagonistic bacteria to be used in biological control of Rhizoctonia solani in tomato. Electron J Biotechnol. 2003;6(2):115-27. https://doi.org/10.2225/vol6-issue2-fulltext-8.

  • 8.

    Podile AR, Prakash AP. Lysis and biological control of Aspergillus niger by Bacillus subtilis AF 1. Can J Microbiol. 1996;42(6):533-8. https://doi.org/10.1139/m96-072.

  • 9.

    Chandrika V. Incidence of Antagonistic Bacillus spp. An eco-friendly aquatic priobiotic from aquaculture pond. The Fourth Indian Fisheries Forum. 1996. p. p.147-50.

  • 10.

    Prado S, Montes J, Romalde JL, Barja JL. Inhibitory activity of Phaeobacter strains against aquaculture pathogenic bacteria. Int Microbiol. 2009;12(2):107-14. [PubMed ID: 19784930].

  • 11.

    Yebra DM, Kiil S, Dam-Johansen K. Antifouling technology—past, present and future steps towards efficient and environmentally friendly antifouling coatings. Prog Organic Coatings. 2004;50(2):75-104. https://doi.org/10.1016/j.porgcoat.2003.06.001.

  • 12.

    Beleneva I, Zhukova N. Seasonal dynamics of cell numbers and biodiversity of marine heterotrophic bacteria inhabiting invertebrates and water ecosystems of the Peter the Great Bay, Sea of Japan. Microbiology. 2009;78(3):369-75. https://doi.org/10.1134/S0026261709030163.

  • 13.

    Youschimizu M, Kimura T, et al. Study on the intestinal microflora of salmonids. Fish Pathol. 1976;10(2):243-259.

  • 14.

    Beleneva IA, Zhukova NV, Le lan H, Ngueyen Tran DH. [Taxonomic composition of bacteria associated with cultivated mollusks Crassostrea lugubris and Perna viridis and with the water of the Gulf of Nha Trang Lagoon, Vietnam]. Mikrobiologiia. 2007;76(2):253-62. [PubMed ID: 17583223].

  • 15.

    Sambrook J, Fritsch E, Maniatis T. Molecular cloning: a laboratory manual. 1989.

  • 16.

    Lane D. Nucleic acid techniques in bacterial systematic. 1991.

  • 17.

    Saitou N, Nei M. The neighbor-joining method: a new method for reconstructing phylogenetic trees. Mol Biol Evol. 1987;4(4):406-25. [PubMed ID: 3447015].

  • 18.

    Kimura M. A simple method for estimating evolutionary rates of base substitutions through comparative studies of nucleotide sequences. J Mol Evol. 1980;16(2):111-20. [PubMed ID: 7463489]. https://doi.org/10.1007/BF01731581.

  • 19.

    Tamura K, Peterson D, Peterson N, Stecher G, Nei M, Kumar S. MEGA5: molecular evolutionary genetics analysis using maximum likelihood, evolutionary distance, and maximum parsimony methods. Mol Biol Evol. 2011;28(10):2731-9. [PubMed ID: 21546353]. https://doi.org/10.1093/molbev/msr121.

  • 20.

    Felsenstein J. Confidence limits on phylogenies: an approach using the bootstrap. Evolution. 1985;39(4):783-91. https://doi.org/10.2307/2408678.

  • 21.

    Giovannoni S, Rappe M. Microbial ecology of the ocean. 2000.

  • 22.

    Giovannoni S, Rappe M, Kirchman D. Microbial ecology of the ocean. 2000.

  • 23.

    Sharma M, Thapaliya H. Antibiotic profiling of heavy metal resistant bacterial isolates from the effluent of a garment industry in Latitpur, Nepal. Our Nature. 2009;7(1):203-6.

  • 24.

    Kwon KK, Lee HS, Jung SY, Yim JH, Lee JH, Lee HK. Isolation and identification of biofilm-forming marine bacteria on glass surfaces in Dae-Ho Dike, Korea. J Microbiol Seoul. 2002;40(4):260-6.

  • 25.

    Nair S, Simidu U. Distribution and significance of heterotrophic marine bacteria with antibacterial activity. Appl Environ Microbiol. 1987;53(12):2957-62. [PubMed ID: 3435149].

  • 26.

    Shakila R, Saravanakumar R, Vyla S, Jeyasekaran G, Jasmine G. Antagonistic activity of the gut microflora isolated from farmed tiger shrimp (Penaeus monodon). Asian Fish Sci. 2006;19(3/4):247.

  • 27.

    Yan L, Boyd KG, Adams DR, Burgess JG. Biofilm-specific cross-species induction of antimicrobial compounds in bacilli. Appl Environ Microbiol. 2003;69(7):3719-27. [PubMed ID: 12839737]. https://doi.org/10.1128/AEM.69.7.3719-3727.2003.

  • 28.

    Palleroni N, Genus I, Kreig N, Holt J. Bergey’s Manual of Systematic Bacteriology. 1984. [PubMed ID: 6501942].

  • 29.

    Rekha VA, John D, Shankar T. [Antibacterial activity of Pseudomonas fluorescens isolated from rhizosphere soil]. Int J Biol Technol. 2010;1(3):10-4.

  • 30.

    Romanenko LA, Tanaka N, Uchino M, Kalinovskaya NI, Mikhailov VV. Diversity and antagonistic activity of sea ice bacteria isolated from the sea of Japan. Microbes Environ. 2008;23(3):209-14. [PubMed ID: 21558710]. https://doi.org/10.1264/jsme2.23.209.

  • 31.

    Uzair B, Ahmed N, Kousar F, Edwards D. Isolation and characterization of Pseudomonas strain that inhibit growth of indigenous and clinical isolate. Internet J Microbiol. 2006;2(2).

  • 32.

    Radjasa O, Martens T, Grossart H, Brinkoff T, Sabdono A, Simon M. Antagonistic activity of a marine bacterium Pseudoalteromonas luteoviolacea TAB4.2 associated with coral Acropora sp. J Biol Sci.

  • 33.

    Onishchenko O. Alteromonas–like bacteria isolated from water and invertebrate animals of the Black Sea and their antagonistic activity. Ekologiya moray. 2001;57:37-40.

  • 34.

    Meziti A, Kormas KA, Pancucci-Papadopoulou MA, Thessalou-Legaki M. Bacterial phylotypes associated with the digestive tract of the sea urchin Paracentrotus lividus and the ascidian Microcosmus sp. Russ J Mar Biol. 2007;33(2):84-91. https://doi.org/10.1134/S1063074007020022.

  • 35.

    Rohwer F, Seguritan V, Azam F, Knowlton N. Diversity and distribution of coral-associated bacteria. Mar Eco Prog Ser. 2002;243(1):1-10. https://doi.org/10.3354/meps243001.

  • 36.

    Bhattarai HD, Lee YK, Cho KH, Lee HK, hin HW. The study of antagonistic interactions among pelagic bacteria: a promising way to coin environmental friendly antifouling compounds. Hydrobiologia. 2006;568(1):417-23.

  • 37.

    Buchan A, Gonzalez JM, Moran MA. Overview of the marine roseobacter lineage. Appl Environ Microbiol. 2005;71(10):5665-77. [PubMed ID: 16204474]. https://doi.org/10.1128/AEM.71.10.5665-5677.2005.

  • 38.

    Porsby CH, Nielsen KF, Gram L. Phaeobacter and Ruegeria species of the Roseobacter clade colonize separate niches in a Danish Turbot (Scophthalmus maximus)-rearing farm and antagonize Vibrio anguillarum under different growth conditions. Appl Environ Microbiol. 2008;74(23):7356-64. [PubMed ID: 18952864]. https://doi.org/10.1128/AEM.01738-08.

  • 39.

    Gana ML, Kebbouche-Gana S, Touzi A, Zorgani MA, Pauss A, Lounici H, et al. Antagonistic activity of Bacillus sp. obtained from an Algerian oilfield and chemical biocide THPS against sulfate-reducing bacteria consortium inducing corrosion in the oil industry. J Industrial microbiol Biotechnol. 2011;38(3):391-404. [PubMed ID: 20949304]. https://doi.org/10.1007/s10295-010-0887-2.