Bacterial biota of shrimp intestine is significantly modified by the use of a probiotic mixture: a high throughput sequencing approach
© The Authors 2017
Received: 12 November 2016
Accepted: 23 March 2017
Published: 8 April 2017
The use of probiotics is a common practice of current shrimp aquaculture. Despite the immunophysiological responses that have been measured in shrimp exposed to probiotics, no information is currently available on the effect of this practice on the intestinal microbiota. The objective of this work was to evaluate the effect of a probiotic mixture on the intestinal microbiota of shrimp cultured under farm conditions. A culture-independent method based on high-throughput-sequencing (16S rRNA) was used to examine intestinal bacterial communities. A traditional system (without probiotics) was used as the reference. Targeted metagenomics analysis revealed that the probiotic mixture was based on bacteria in the phyla Proteobacteria and Firmicutes. A total of 23 species of bacteria were detected in the probiotic mixture; of these, 11 were detected in the intestine of shrimp reared in both systems, and 12 were novel for the system. Eight of the novel species were detected in shrimp cultured with the probiotic mixture; however, none of these novel species were related to marine or inclusively aquacultural environments, and only one (Bacillus subtilis) was recognized as probiotic for shrimp. The use of the probiotic mixture modified the bacterial profile of the shrimp intestine; however, most of the bacteria incorporated into the intestine were nonindigenous to the marine environment with no previous evidence of probiotic effects on any marine organism. The use of this probiotic mixture may represent a risk of causing environmental imbalances, particularly because farms using these types of probiotic mixtures discharge their effluents directly into the ocean without prior treatment.
KeywordsAquaculture Bacterial diversity Intestinal microbiota Metagenomics Probiotics
Pathogens have undermined shrimp aquaculture [1, 2], and for the past two decades, antibiotic use has been the most important and effective strategy to control and prevent bacterial infections [3, 4]. However, the use of antibiotics may have negative consequences for human and environmental health, inducing resistance to antibiotics and promoting transference of antibiotic resistance genes [5, 6].
A wide diversity of marine pathogens can develop plasmid-mediated resistance. For example, plasmids containing genes for antibiotic resistance have been detected in marine species associated with aquaculture [7, 8]. The presence and transfer of plasmids containing antibiotic resistance genes may cause a continuous decrease in antibiotic effectiveness, which is usually an expensive resource.
Therefore, strategies aimed at controlling disease and improving shrimp health are required. The use of probiotics is one of the most promising alternatives . The consensus defines probiotics as living microorganisms that confer any health benefit on the host by diverse mechanisms, including improvement in intestinal balance, delivery of certain enzymes to the intestine for digestion purposes, production of chemicals that inhibit or decelerate the growth of possible pathogens, competition against pathogens for resources and/or enhancement of the immune response of the host [9, 10].
Therefore, probiotics can be introduced into the culture environment to control and compete with pathogenic bacteria and to promote the growth of the cultured organisms . However, most of the research on the use of probiotics, including that of commercial products, has focused on the physiological and immunological responses of the host, in addition to host resistance to pathogen challenges and production performance [11–13].
Although these responses are important economic considerations; no extensive evidence regarding the effect of these products on the host microbiota is available, which is one of the primary targets of probiotics. Understanding the effects of probiotic use on intestinal microbiota is critically important to comprehend the effect of these strategies on shrimp aquaculture, considering the multiple guest–host functions in which intestinal microbiota participate (i.e., metabolic, trophic and protective functions) [2, 14]. Therefore, comprehension of the biology of a cultured organism may represent a guarantee of success. Furthermore, changes in microbiota induced by the use of probiotics may be beneficial to shrimp, but a risk also occurs that the changes will affect microbial communities with important functions for these crustaceans.
Probiotic products are used indiscriminately in very different environmental conditions . However, this strategy may be inadequate given that some of the bacteria species contained in these products may not be adapted to the marine ecosystem and are most likely incapable of thriving in the conditions generated within shrimp/fish ponds. Finally, risks are also associated with the introduction of nonindigenous species into the marine ecosystem; for example, probiotics can contain plasmids with antibiotic resistance genes [15, 16]. Therefore, it is also important to identify the bacteria species that are introduced into open aquaculture systems.
The aim of this research was to study the effect of a probiotic mixture used in shrimp farms on the intestinal bacterial biota (16S rRNA) of shrimp.
Shrimp (Litopenaeus vannamei) weighing 0.3 ± 0.04 g were stocked at 35 shrimp m−2 in 2 ha earthen ponds 1.5 m in depth. Organisms were fed twice a day at 4% of daily wet biomass·day−1 with commercial feed containing 35% crude protein (PURINA®). Water temperature oscillated between 25 and 32 °C, with dissolved oxygen (DO) at 4–6 mg L−1, salinity at 38-40 PSU, and pH values of 7.9–8.6. Paddle aerators were used during the night, and a daily water exchange ratio of 10% was performed using water directly from the ocean. Twelve ponds were selected for the study: six using the probiotic mixture and six without addition of probiotics.
Eight bioreactors (10,000 L each) were used at full capacity on the farm to promote the growth of probiotic bacteria. Bioreactors were designed to improve the proliferation of aerobic bacteria; the culture media was constantly mixed by axial flow, and air micro bubbles were injected at the bottom of the reactors.
Bioreactors were inoculated with a commercial probiotic product based on a Bacilli- and Gamma-proteobacteria mixture (Eco-AQUAPROTEC, Australia). The bacterial profile based on 16S rRNA (regions v3-v4) is presented below (Fig. 1). Briefly, the water used for the bioreactors was filtered by flow through one-micron sand filters and then was sterilized by eight UV lamps. Probiotic cultures were grown under constant light conditions (100 μmol photon/m2/s, 500 nm) to enhance the proliferation of autotrophic bacteria. The bio-catalyzer design was based on the fermentation of organic material, including cow manure, vegetal substrate and other ingredients (not revealed by the company), aimed at producing oxygen and hypersaline-adapted enzymes. This phenomenon was achieved by maintaining a constant pressure (500 millibar) with hyperbaric columns on the side of the bioreactors.
A carbon:nitrogen:phosphorus ratio of 20:3:1 was maintained in each reactor by adding molasses as a carbon source (20 L), NaNO3 (2 kg) and (NH4)2SO4 (1 kg) as nitrogen sources, and KH2PO4 (0.5 kg) and K2HPO4 (0.5 kg) as phosphorus sources. The pH was up-regulated by the addition of NaOH (≤1 kg) 1 h before the inoculation (Na2CO3 was used during the bacterial culture). Physicochemical conditions were maintained at 30 °C, with dissolved oxygen at 4 mg L−1 and a pH of 7.5 (adjusted every 3 h). Once these conditions were met, the probiotic was inoculated at a density of ≈25,000 cells mL−1. Bacterial cell counts reached the maximum concentration at 24 h, registering 1 × 1012 CFU mL−1 for the probiotic mixture. Once the maximum concentration was attained, the probiotic mixture was ready for use in the shrimp culture units.
A volume of 150 L of probiotic mixture was added directly to the water of each pond on the farm daily (except for the six reference ponds), and the reactors were prepared to amass bacteria again.
The bacterial diversity of the probiotic mixture and shrimp intestines was monitored with a targeted loci approach on two sample dates using the 16S rRNA gene and considering the hypervariable regions V3 and V4. Alpha (α) and beta (β) diversity was calculated using a analytic hierarchy method described by Goepel  and using the Shannon-index and relative homogeneity values as parameters.
Shrimp intestines were obtained on the 30th and 60th days of culture. Six earthen ponds for each culture system were used for the study, and 10 shrimp intestines·pond−1 were sampled on the above dates using 50-mL sterile falcon tubes (VWR, USA) and then stored at −80 °C. Intestine samples from the same ponds were pooled, and ponds were the replicates.
Nucleic acids isolation
DNA was isolated from the probiotic mixture and shrimp intestines. Intestines were dissected from the rest of the carcass and longitudinally cut; intestines were washed with sterile/nuclease-free water to remove fecal matter and transient-unattached microorganisms. Thereafter, the probiotic mixture and the intestine samples from each culture system were homogenized at 6 m s−1 in a FastPrep-24™ 5G homogenizer (MP Biomedicals, USA). The commercial Meta-G-Nome™ DNA isolation kit (Epicentre, USA) was used for the isolation of randomly sheared, high molecular weight metagenomic DNA (free of humic and fulvic acids) directly from unculturable or difficult-to-culture bacteria in shrimp intestines.
To isolate DNA from the probiotic mixture, 10 mL of the mixture was filtered through a 0.45-μm membrane (Millipore, USA); from this step forward, the instructions used with the above DNA isolation kit were strictly followed for all samples.
The quality of the DNA isolates was monitored with a 2200 Tapestation microfluidic electrophoresis instrument (Agilent, USA). Briefly, 1 µL of DNA isolate solution was mixed with 10 µL of gDNA sample buffer (Agilent, USA), and a gDNA Ladder (Agilent, USA) was used as the reference. From the mixture, 1 µL per sample was inserted into a microfluidic chip (gDNA ScreenTape, Agilent, USA) for the analysis of 200–>60,000-bp DNA fragments. Finally, the microfluidic chip containing the nucleotide samples was inserted into a 2200 Tapestation Electrophoresis Instrument (Agilent, USA). All the samples with DNA integrity numbers above 7 were considered for the following library preparation.
16S Amplicon PCR Forward Primer (Bakt_341F) + Overhang adapter = 5′-TCGTCGGCAGCGTCAGATGTGTATAAGAGACAGCCTACGGGNGGCWGCAG-3′;
16S Amplicon PCR Reverse Primer (Bakt_805R) + Overhang adapter = 5′-GTCTCGTGGGCTCGGAGATGTGTATAAGAGACAGGACTACHVGGGTATCTAATCC-3′.
A first amplification step was performed in 25-μL reactions using 2× KAPA HiFi HotStart ReadyMix (KAPA Biosystems, USA) under the following thermal cycling conditions: one initial denaturation step at 95 °C for 3 min; 25 cycles at 95 °C for 10 s, at 55 °C for 30 s, and at 72 °C for 30 s; an extension at 68 °C for 5 min; and a hold step at 4 °C. Thereafter, the resulting amplicons (450–550 bp) were submitted to a cleanup procedure using magnetic AMPure XP beads (Beckman Coulter, USA) to purify the amplicons from free primers and primer dimer species, following the manufacturer’s specifications. Once the amplicons were cleaned, they were attached with dual indices and sequencing adapters using the Nextera XT Index Kit (Illumina, USA) and 2× KAPA HiFi HotStart ReadyMix. The above thermal cycling conditions were performed for 8 cycles, and the above process using AMPure XP beads was repeated to again clean up the library. Finally, the resulting library was quantified and qualified by capillary electrophoresis (2200 Tapestation, Agilent, USA) using microfluidic chips (D1000 Screen Tape, Agilent, USA) with an analysis range of 35–1000 bp. Briefly, 2 µL of indexed library samples was mixed with 2 µL of High Sensitivity D1000 buffer. These samples were loaded into High Sensitivity D1000 screentapes and analyzed using the 2200 Tapestation instrument.
All the libraries were adjusted to a concentration of 4 nM using 10 mM Tris (pH 8.5) as diluent and pooled in the same proportion. Thereafter, libraries were denatured with 0.2 N NaOH. A standard PhiX Control Library (Illumina, USA) was also denatured and used as an internal control. Both the denatured library and PhiX Control were adjusted to a concentration of 8 pM and mixed (95% library + 5% PhiX Control). Finally, the mixture was heated to 96 °C for 2 min and immediately cooled on ice for 5 min.
The sample was then loaded into a MiSeq v3 Reagent Tray (Illumina, USA) and inserted into a MiSeq sequencing instrument (Illumina, USA), which contained a MiSeq v3 Flow Cell (Illumina, USA) with a capacity of 25 million reads. The results were obtained after 300 cycles.
All sequences were submitted to taxonomic classification. Ultrafast-metagenomic sequence classification using exact alignments (Kraken) was performed in the Illumina BaseSpace platform (basespace.illumina.com). A phylotype-based analysis was performed instead of using an OTU-based approach considering the superior classification performance reported in recent studies [19, 20]. Kraken maps each single sequence to the lowest common ancestor in the database and performs alignments of matching sequences, forming a subtree whose nodes have a specific weight equal to the number of sequences associated with the node’s taxon; finally, the subtree is used for classification.
Data of relative abundance of each bacterial species were analyzed using a repeated-measures analysis of variance, considering culture system as the main factor in the hierarchical linear modeling, and a significance level of p = 0.05.
A total of 2,482,431 reads were generated for the probiotic sample. Approximately 74% of the reads were classified to order, 40% to family, and ~35% to genus and species.
With respect to intestine samples, an average of 150,000 reads per sample was obtained from which ~60% were assigned to order, 45–55% to family, and 35–40% to genus and species.
Targeted metagenomics analysis of the probiotic mixture revealed that it was primarily composed of bacteria in the phyla Proteobacteria (primarily order Gammaproteobacteria) and Firmicutes (primarily Bacilli) (Fig. 1) and a smaller proportion of bacteria from diverse phyla.
Alpha diversity values were 1.64 and 2.03 (Shannon-index) for shrimp reared in the traditional and the probiotic-based systems, respectively, with relative homogeneity values of 98.7 and 93.5%, respectively. Regarding β-diversity, the Shannon-index value was 0.36, and the relative homogeneity was 39.7%.
Bacteria species detected in the probiotic mixture and their detection in shrimp reared in the probiotic-based system (using the mixture) and in the traditional system
Species detected in the probiotic mixture
Sphingobacterium ingobacterium sp.
Nocardioides ardioides sp.
Borrelia relia sp.
Proportion of reads (v3–v4, 16S rRNA) assigned to species level in samples of shrimp reared in the traditional system (no probiotics) and in the probiotic-based system
35.5 ± 1.9
37.5 ± 1.1
4.9 ± 0.6
7.7 ± 0.5
26.5 ± 1.2
27.5 ± 0.6
15.0 ± 1.0
6.1 ± 0.2
16.5 ± 0.6
15.5 ± 0.8
1.4 ± 0.3
0.8 ± 0.1
7.1 ± 0.1
6.9 ± 0.2
0.1 ± 0.1
0.1 ± 0.0
5.5 ± 0.7
6.9 ± 0.3
1.2 ± 0.1
1.4 ± 0.6
3.5 ± 0.3
3.4 ± 0.2
3.6 ± 0.3
3.6 ± 0.1
0.3 ± 0.1
0.3 ± 0.1
0.1 ± 0.1
5.7 ± 0.4
0.3 ± 0.1
0.3 ± 0.1
29.7 ± 2.1
25.1 ± 0.7
0.1 ± 0.1
0.3 ± 0.1
2.7 ± 0.2
4.2 ± 0.3
0.1 ± 0.1
0.1 ± 0.0
10.4 ± 1.3
5 ± 1.1
0.1 ± 0.1
0.1 ± 0.1
7.9 ± 1.2
16 ± 1.5
0 ± 0.00
0 ± 0.00
3.9 ± 0.6
0.7 ± 0.2
4.5 ± 0.7
1.2 ± 0.5
19.3 ± 1.3
23.6 ± 1.5
Regarding phyla level, a high proportion of Proteobacteria was detected in the intestines of shrimp from both treatments. Higher proportions of Proteobacteria (particularly the class Alphaproteobacteria) and Bacteroidetes were detected in the intestines of shrimp reared in the probiotic-based system than in those of shrimp cultured without probiotics. Additionally, lower proportions of Planctomycetes, Actinobacteria and Firmicutes were detected in the intestines of shrimp from the probiotic-based system than in those of the traditional system (Fig. 3).
The most evident differences between treatments were detected in the fraction of reads assigned to a genus or species. For example, a total of 23 different species were detected in the probiotic mixture in different proportions (Table 1); of these, 11 were also detected in the intestines of shrimp reared in both systems, but 12 were completely novel for the systems. None of these novel species were detected in shrimp reared in the traditional system, but eight were detected in shrimp cultured with the probiotic mixture, which included Methylomonas methanica, Pseudomonas stutzeri, Pseudoxanthomonas suwonensis (all Proteobacteria), Bacillus subtilis, Geobacillus thermoleovorans (Firmicutes), Sphingobacterium ingobacterium sp. (Bacteriodetes), Oceanithermus profundus (Deinococcus-Thermus) and Mycoplasma synoviae (Tenericutes) (Table 1).
Bacteria species detected exclusively in shrimp reared in the traditional and probiotic-based systems on the 30th and 60th days
Changes in the intestinal bacterial profile of shrimp reared in the probiotic-based system on the 30th and 60th days
Detected on the 30th day only
Detected on the 60th day only
With respect to abundance, T. whipplei, Rhodopirellula baltica, I. coccineus, M. adhaerens and P. acanthamoebae represented approximately 95% of the reads assigned to the level of species detected in shrimp cultured within the traditional system, whereas T. whipplei, R. baltica, Rhudobacter capsulatus, P. brasilensis, K. vulgare and P. stutzeri represented 85% of the reads in shrimp from the probiotic-based system (Fig. 4).
Microbial identification in animal husbandry and agriculture is meaningful only when microbiota can be classified to the level of genus or species . The classification of 35–40% of the reads to a genus or species was a successful result, considering that only a small fraction of all 16S gene sequences belonging to unculturable bacteria are registered in databases .
Alpha diversity analysis revealed that the bacterial profile was uniform within samples of both treatments, whereas β-diversity and relative homogeneity demonstrated that the use of probiotics had an effect on the intestinal microbiota. For example, probiotic use favored the growth of Proteobacteria and inhibited that of Planctomycetes.
Proteobacteria, Planctomycetes, Actinobacteria, Firmicutes and Chlamydiae colonized the intestines of shrimp reared without probiotics, but the probiotics favored the growth of Proteobacteria and inhibited that of Planctomycetes. Most of these phyla, except for Planctomycetes, have been previously reported as natural microbiota of the intestines of penaeid shrimp [2, 14].
Although the colonization of novel bacteria species in the intestines of shrimp from the probiotic-based system could represent a good indicator of probiotic functioning, these new bacteria and the associated modifications of the microbiota of the intestines must be analyzed. Several bacterial species contained in the probiotic that also colonized the intestinal tract of shrimp are currently not associated with the marine environment and have not been recognized as probiotics. For example, M. methanica is considered a methanotrophic symbiont that thrives in both freshwater and marine ecosystems but particularly in methane-producing sludge . Although toxic compounds such as hydrogen sulfide and methane are produced in the bottom of shrimp ponds, this risk can be eliminated by adequate management practices. Therefore, there is no evidence that this type of bacterium could promote any probiotic effect in shrimp intestines. P. suwonensis is an organophosphate- and cellulose-degrading bacteria commonly detected in woody environments . Sphingobacterium sp. is a gram-negative, strictly aerobic, chemoorganotrophic bacterium that has been isolated from terrestrial environments and aerobic sludge and is capable of degrading acetanilide herbicide ; some strains have been detected in fish aquaculture systems, but their role remains unclear. Mycoplasma synoviae is a gram-negative bacterium pathogenic for several poultry species, and there are no reports associating this species with any marine animal or environment. Oceanithermus profundis is a gram-negative, thermophilic, organotrophic, chemolithotrophic bacterium isolated from deep-sea hydrothermal vents . Some of these bacteria are commonly used for their biodegradation properties; however, there is no evidence that they have any probiotic effects in shrimp or other marine animal.
Among the bacteria that colonized shrimp intestine, P. stutzeri reportedly participates in denitrification processes, reducing nitrate to dinitrogen gas . This Proteobacteria demonstrates inhibitory effects against Vibrio parahemolitycus (ATCC 17802), V. alginolyticus (ATCC 17749) and V. alginolyticus (S1) in aquatic organisms . B. subtilis is perhaps the only one of these species that is recognized as a probiotic for penaeids because of inhibitory effects against some pathogens . G. thermoleovorans is an extreme thermophile with antibacterial activity against human pathogens that possesses enzymes such as phosphatase alkaline, esterase lipase, amylase, lipase, lecitenase and caseinase ; however, it is not known whether this bacterium has any antibacterial effects on marine pathogens.
It is possible that some of these bacteria (most of them not from a marine environment) are capable of colonizing shrimp intestines because of their physiological plasticity. Some of these bacteria have been isolated from extreme environments. Despite the successful colonization of some of these bacteria in the intestine, bacteria thriving in the immediate environment of marine species may have a much greater influence on the health and pathogen resistance of shrimp than that of allochthonous bacteria whose colonization is achieved by the constant addition of the probiotic mixture. These results revealed a possible alarming scenario because most shrimp farms include open systems, and farmers using this type of product or performing similar practices may be introducing nonindigenous bacterial species into the marine environment.
The effect of the probiotic mixture on the intestinal microbiota must be analyzed based on the idea of Mahdhi et al. , who argued that “probiotics are live microbial feed supplements, improving the intestinal balance of the host and producing metabolites which inhibit the colonization or growth of other microorganisms or by competing with them for resources such as nutrients or space.” In this regard, a modification of the microbiota (presence and abundance) was detected when shrimp were exposed to the probiotic mixture; however, the abundance of some marine and native bacteria decreased in shrimp exposed to the probiotic mixture. For example, the proportion of R. baltica, which is a marine aerobic heterotrophic bacterium usually detected in aquaculture farms and marine environments that plays a role in the nitrogen cycle and biodegradation of organic material, decreased . By contrast, R. capsulatus, which possesses a wide range of metabolic capabilities and some antibacterial activity against gram-negative bacteria , increased. Additionally, Pseudovibrio sp., which has some antibacterial activity against marine sponge pathogens also increased.
It is difficult to conclude whether these changes in bacterial proportions corresponded to a positive or to a negative effect of the probiotic mixture. Earlier experiments in our laboratory revealed that this probiotic mixture enhances some of the immune responses of shrimp, but it was not possible to elucidate which of the tens of different bacteria contained in the mixture caused the effect . Moreover, enhancing immune responses with nonindigenous species is not a guarantee of health and could require an unnecessary expenditure of energy.
For shrimp reared with probiotics, the differences between the 30th and 60th day suggested that a lower dose of probiotics should be used. The modification of microbiota may favor the proliferation of other species, as was observed in this experiment; however, the constant addition of bacteria (mostly nonindigenous) to shrimp also entails a constant addition to the marine environment.
None of the bacteria identified (except for the genus Bacillus) is recognized in the literature as a probiotic for crustaceans. As stated above, probiotic mixtures should be based on microorganisms isolated from similar and preferably immediate environments to the host.
A common strategy to obtain this type of bacteria is to perform in vitro antagonism tests, exposing pathogens to alleged probiotics. Although this in vitro strategy may not provide 100% confidence because some probiotics may behave differently in vivo and in aquaculture systems, this strategy could be a first approach to study the identified candidates. Other approaches may include the exposure of hosts reared with particular probiotics to pathogen challenges.
The bacterial diversity observed in shrimp, both cultured with and without probiotics, revealed that species in the phyla Proteobacteria, Firmicutes, Bacteriodetes, Actinobacteria, Planctomycetes, Chlamydiae and Cyanobacteria composed the regular microbiota of shrimp; some of these may constitute first case reports for the species.
Finally, one notable concern was that some human bacterial pathogens were identified, including T. whipplei, P. acanthamoebae and S. enterica, which are usually detected in human feces, wastewater, and contaminated food. Although whether the bacteria detected corresponded to pathogenic strains could not be determined, this finding constitutes a first case report of this type of bacteria (in addition to others in this study) in shrimp aquaculture systems. One possible explanation for these bacteria is the practice of open farms performing water exchanges by taking water directly from the ocean without previous treatment.
- 16S rRNA:
ribosomal 16S RNA gene
colony forming units
MPC, MMP and FVA conceived the study; MPC, EVC and TGG performed the experiment, sampling and all the analyses and handling of data. MPC, MMP, FVA, TGG and LRMC contributed to data interpretation. MMP and LRMC wrote the manuscript. All authors read and approved the final manuscript.
Special thanks are offered to M.S. Miguel Antonio Arvayo-Porchas for his contribution in the execution of this experiment.
The authors declare that they have no competing interests.
Availability of data and materials
Data will be available at https://www.dropbox.com/home/Helgoland%20Marine%20Research.
Consent for publication
All authors read and approved the final manuscript.
Centro de Investigación en Alimentación y Desarrollo A.C. Internal Project.
Open AccessThis article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.
- Martinez-Porchas M, Martinez-Cordova LR. World aquaculture: environmental impacts and troubleshooting alternatives. Sci World J. 2012;2012:389623. doi:10.1100/2012/389623
- Tzuc JT, Escalante DR, Herrera RR, Cortés GG, Ortiz MLA. Microbiota from Litopenaeus vannamei: digestive tract microbial community of Pacific white shrimp (Litopenaeus vannamei). SpringerPlus. 2014;3:280.View ArticlePubMedPubMed CentralGoogle Scholar
- Burridge L, Weis JS, Cabello F, Pizarro J, Bostick K. Chemical use in salmon aquaculture: a review of current practices and possible environmental effects. Aquaculture. 2010;306:7–23.View ArticleGoogle Scholar
- Cabello FC. Heavy use of prophylactic antibiotics in aquaculture: a growing problem for human and animal health and for the environment. Environ Microbiol. 2006;8:1137–44.View ArticlePubMedGoogle Scholar
- Cabello FC, Godfrey HP, Tomova A, Dölz H, Millanao A. Antimicrobial use in aquaculture re-examined: its relevance to antimicrobial resistance and to animal and human health. Environ Microbiol. 2013;15:1917–42.View ArticlePubMedGoogle Scholar
- Sharifuzzaman S, Austin B. Influence of probiotic feeding duration on disease resistance and immune parameters in rainbow trout. Fish Shellfish Immunol. 2009;27:440–5.View ArticlePubMedGoogle Scholar
- Balcázar J, De Blas I, Ruiz-Zarzuela I, Cunningham D, Vendrell D, Múzquiz J. The role of probiotics in aquaculture. Vet Microbiol. 2006;114:173–86.View ArticlePubMedGoogle Scholar
- Carvalho FCT, Sousa OV, Carvalho EMR, Hofer E, Vieira RHSF. Antibiotic resistance of Salmonella spp. isolated from shrimp farming freshwater environment in northeast region of Brazil. J Pathog. 2013;2013:685193. doi:10.1155/2013/685193
- Mahdhi A, Hmila Z, Behi A, Bakhrouf A. Preliminary characterization of the probiotic properties of Candida famata and Geobacillus thermoleovorans. Iran J Microbiol. 2011;3:129–34.PubMedPubMed CentralGoogle Scholar
- Sanders M. Probiotics: definition, sources, selection, and uses. Clin Infect Dis. 2008;46:S58–61.View ArticlePubMedGoogle Scholar
- Farzanfar A. The use of probiotics in shrimp aquaculture. FEMS Immunol Med Microbiol. 2006;48:149–58.View ArticlePubMedGoogle Scholar
- Akhter N, Wu B, Memon AM, Mohsin M. Probiotics and prebiotics associated with aquaculture: a review. Fish Shellfish Immunol. 2015;45:733–41.View ArticlePubMedGoogle Scholar
- Hai NV. The use of probiotics in aquaculture. J Appl Microbiol. 2015;119:917–35.View ArticlePubMedGoogle Scholar
- Rungrassamee W, Klanchui A, Maibunkaew S, Chaiyapechara S, Jiravanichpaisal P, Karoonuthaisiri N. Characterization of intestinal bacteria in wild and domesticated adult black tiger shrimp (Penaeus monodon). PLoS ONE. 2014;9:e91853.View ArticlePubMedPubMed CentralGoogle Scholar
- Uddin G, Larsen M, Christensen H, Aarestrup F, Phu T, Dalsgaard A. Identification and antimicrobial resistance of bacteria isolated from probiotic products used in shrimp culture. PLoS ONE. 2015;10:e0132338.View ArticleGoogle Scholar
- Sharma P, Tomar S, Goswami P, Sangwan V, Singh R. Antibiotic resistance among commercially available probiotics. Food Res Int. 2014;57:176–95.View ArticleGoogle Scholar
- Goepel KD. Implementing the analytic hierarchy process as a standard method for multi-criteria decision making in corporate enterprises: a new AHP excel template with multiple inputs. In: Proceedings of the international symposium on the analytic hierarchy process; 2013, 1–10.
- Herlemann D, Labrenz M, Jürgens K, Bertilsson S, Waniek J, Andersson A. Transitions in bacterial communities along the 2000 km salinity gradient of the Baltic Sea. ISME J. 2011;5:1571–9.View ArticlePubMedPubMed CentralGoogle Scholar
- Martínez-Porchas M, Villalpando-Canchola E, Vargas-Albores F. Significant loss of sensitivity and specificity in the taxonomic classification occurs when short 16S rRNA gene sequences are used. Heliyon. 2016;2:e00170.View ArticlePubMedPubMed CentralGoogle Scholar
- Valenzuela-González F, Martínez-Porchas M, Villalpando-Canchola E, Vargas-Albores F. Studying long 16S rDNA sequences with ultrafast-metagenomic sequence classification using exact alignments (Kraken). J Microbiol Methods. 2016;122:38–42.View ArticlePubMedGoogle Scholar
- Petrosino J, Highlander S, Luna R, Gibbs R, Versalovic J. Metagenomic pyrosequencing and microbial identification. Clin Chem. 2009;55:856–66.View ArticlePubMedPubMed CentralGoogle Scholar
- Martinez-Porchas M, Vargas-Albores F. Microbial metagenomics in aquaculture: a potential tool for a deeper insight into the activity. Rev Aquac. 2017;9:1–9.View ArticleGoogle Scholar
- Guri M, Durand L, Cueff-Gauchard V, Zbinden M, Crassous P, Shillito B, et al. Acquisition of epibiotic bacteria along the life cycle of the hydrothermal shrimp Rimicaris exoculata. ISME J. 2012;6:597–609.View ArticlePubMedGoogle Scholar
- Hou L, Jiang J, Xu Z, Zhou Y, Leung FC-C. Complete genome sequence of Pseudoxanthomonas suwonensis strain J1, a cellulose-degrading bacterium isolated from leaf-and wood-enriched soil. Genome Announc. 2015;3:e00614-15.View ArticlePubMedPubMed CentralGoogle Scholar
- Ye Y, Min H, Du Y. Characterization of a strain of Sphingobacterium sp. and its degradation to herbicide mefenacet. J Environ Sci. 2003;16:343–7.Google Scholar
- Fedosov D, Podkopaeva D, Miroshnichenko M, Bonch-Osmolovskaya E, Lebedinsky A, Grabovich MY. Metabolism of the thermophilic bacterium Oceanithermus profundus. Microbiology. 2008;77:159–65.View ArticleGoogle Scholar
- Zumft W, Braun C, Cuypers H. Nitric oxide reductase from Pseudomonas stutzeri. Eur J Biochem. 1994;219:481–90.View ArticlePubMedGoogle Scholar
- Abdelkarim M, Kamel C, Fathi K, Amina B. Use of Pseudomonas stutzeri and Candida utilis in the improvement of the conditions of Artemia culture and protection against pathogens. Braz J Microbiol. 2010;41:107–15.View ArticlePubMedPubMed CentralGoogle Scholar
- Balcázar J, Rojas-Luna T. Inhibitory activity of probiotic Bacillus subtilis UTM 126 against Vibrio species confers protection against vibriosis in juvenile shrimp (Litopenaeus vannamei). Curr Microbiol. 2007;55:409–12.View ArticlePubMedGoogle Scholar
- Lage O, Bondoso J, Viana F. Isolation and characterization of Planctomycetes from the sediments of a fish farm wastewater treatment tank. Arch Microbiol. 2012;194:879–85.View ArticlePubMedGoogle Scholar
- Lee S-S, Oh TJ, Kim J, Kim J-B, Lee H-S. Bacteriocin from purple nonsulfur phototrophic bacteria, Rhodobacter capsulatus. J Bacteriol Virol. 2009;39:269–76.View ArticleGoogle Scholar