Next Article in Journal
A New Kayfunavirus-like Escherichia Phage vB_EcoP-Ro45lw with Antimicrobial Potential of Shiga Toxin-Producing Escherichia coli O45 Strain
Previous Article in Journal
Phytoplankton Community Response to Environmental Factors along a Salinity Gradient in a Seagoing River, Tianjin, China
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Atlantic Salmon (Salmo salar) Transfer to Seawater by Gradual Salinity Changes Exhibited an Increase in The Intestinal Microbial Abundance and Richness

by
María F. Morales-Rivera
1,2,
Diego Valenzuela-Miranda
1,2,3,
Gustavo Nuñez-Acuña
1,2,
Bárbara P. Benavente
1,2,
Cristian Gallardo-Escárate
1,2 and
Valentina Valenzuela-Muñoz
1,2,3,*
1
Interdisciplinary Center for Aquaculture Research (INCAR), University of Concepción, Concepcion 4030000, Chile
2
Laboratory of Biotechnology and Aquatic Genomics, Department of Oceanography, University of Concepción, Concepcion 4030000, Chile
3
Centro de Biotecnología, Universidad de Concepción, Concepcion 4030000, Chile
*
Author to whom correspondence should be addressed.
Microorganisms 2023, 11(1), 76; https://doi.org/10.3390/microorganisms11010076
Submission received: 26 October 2022 / Revised: 7 December 2022 / Accepted: 20 December 2022 / Published: 27 December 2022
(This article belongs to the Topic Microorganisms in Aquatic Environments)

Abstract

:
The host’s physiological history and environment determine the microbiome structure. In that sense, the strategy used for the salmon transfer to seawater after parr-smolt transformation may influence the Atlantic salmon’s intestinal microbiota. Therefore, this study aimed to explore the diversity and abundance of the Atlantic salmon intestinal microbiota and metagenome functional prediction during seawater transfer under three treatments. One group was exposed to gradual salinity change (GSC), the other to salinity shock (SS), and the third was fed with a functional diet (FD) before the seawater (SW) transfer. The microbial profile was assessed through full-16S rRNA gene sequencing using the Nanopore platform. In addition, metagenome functional prediction was performed using PICRUSt2. The results showed an influence of salinity changes on Atlantic salmon gut microbiota richness, diversity, and taxonomic composition. The findings reveal that GSC and the FD increased the Atlantic salmon smolt microbiota diversity, suggesting a positive association between the intestinal microbial community and fish health during seawater transfer. The reported knowledge can be applied to surveil the microbiome in smolt fish production, improving the performance of Atlantic salmon to seawater transfer.

1. Introduction

Over the past years, it has gained consensus that fish health and welfare are highly influenced by their microbiota [1]. The microbiota of marine fish can play pivotal roles in gut development, metabolism, and immune responses. Understanding how microbiomes are modified is important to understand the host-microbe interactions and their influence on host health [2]. Therefore, different research efforts have been focused on understanding the factors that shape gut microbiota in marine fish to promote healthy organisms and welfare in aquaculture production [3].
The fish microbial community has mainly been explored by molecular methods based on sequencing technologies. Herein, the sequencing of the hypervariable regions from V1 to V9 of the 16S rRNA gene was used to study the microbial diversity of marine environments [4,5,6,7]. There is no consensus on which regions should be used to assess the fish microbiota. Thus, it is possible to find studies that use different regions of the 16S rRNA gene for microbiota identification [8,9,10]. However, it is known that the sequencing part of hypervariable regions may affect the taxonomic diversity estimation [11,12,13]. In addition, it has been observed that different 16S rRNA regions alone are not sufficient for precise estimates of richness and higher-level taxonomic classification [14,15]. In recent years, the sequencing of the full 16S rRNA gene with Nanopore technology (Oxford Nanopore Technologies, Oxford, UK) has been suggested as the best tool to identify microbiota for species and higher taxonomic levels [16,17,18,19].
The microbiota structure can be modulated by diverse factors, including host physiological history, diet, ecological factors, and environment, among others [20,21,22]. Regarding environmental factors, it has been evidenced that changes in salinity can influence the structure and diversity of fish gut microbiota [23,24]. In euryhaline fish, the transfer to SW triggers fish drink rate increase [2,25]. These adaptations stabilize osmotic pressure alteration in the gut, which causes changes in the bacterial community that composes the gut microbiota [2,10,26,27].
In Chile, Atlantic salmon (Salmo salar) is the preferred species of salmonids on farms, accounting for 72% of production [28]. During parr-smolt transformation, or smoltification, Atlantic salmon require molecular and physiological changes that allow the fish to change from FW to SW [25,29]. In natural conditions, salmonids pass through a salinity gradient from the river to the sea during smoltification [30]. However, in productive systems, smolts are often transferred from FW to SW directly, without considering the impact of a direct change in salinity in the salmon microbiota and health. A larger diversity and richness of the skin microbiota in SW has been reported when compared with the FW phase one and four weeks after SW migration [8]. Wang et al. [10] reported a high difference in the Atlantic salmon gut microbiota between fish in FW and fish two weeks after the SW transfer. Among their results, a high abundance of the genera Lactobacillus and Photobacterium, associated with FW, and Lactobacillus and Mycoplasma was observed after 22 weeks in SW. Furthermore, in recirculating aquaculture systems [31], gut microbial richness decrees one week after SW has been observed [9]. In addition, it has been reported that microbial community changes in Atlantic salmon during the SW transfer can induce the fish immune system to allow an infectious disease outbreak [31]. Thus, functional diets have been developed to enhance salmonids’ performance and health during smoltification [32].
Previously, we reported transcriptome variation between the Atlantic salmon intestine exposed to gradual salinity change and salinity shock [33]. The study reported a high number of transcripts differentially expressed in the intestinal tissue of salmon exposed to a gradual salinity change compared with fish exposed to salinity shock. Furthermore, a Gen Ontology (GO) enrichment analysis showed a high abundance of genes associated with metabolic processes, ion transmembrane transport, and immune response. Thus, it is possible to suggest changes in the Atlantic salmon intestine microbiota under different smoltification strategies. Therein, this study aimed to explore the intestine microbiota richness and abundance in Atlantic salmon smolts at genus and species level by full 16S rRNA gene Nanopore sequencing. We hypothesized that the different salinity conditions and the use of in-feed functional ingredients could modulate the microbiome community during parr-smolt transfer. Collectively, the findings can support novel strategies for smolt production, improving animal health and welfare in salmon aquaculture.

2. Materials and Methods

2.1. Experimental Design

The Atlantic salmon intestine samples for this study were taken from the assays reported previously for our group [33]. Briefly, freshwater (FW) smolts (60 ± 6.2 g) were obtained from a commercial farm (Hendrix Genetics Aquaculture, Villarrica, Chile) and transported to the Marine Biology Station, Universidad de Concepción, Dichato, Chile. Fish were maintained in ultraviolet-treated by single-pass flow-through tank systems (500 L, 30 fish/tank) on a 12:12 h light: dark cycle, with a dissolved oxygen level of 8.5 mg/L and pH = 8.0, fed daily with a regular diet of Cargill. After one month of acclimation, FW (control group) samples were taken. Then, the fish were separated into three experimental groups in triplicate. The first group of salmons, 30 smolts per tank in triplicate, was exposed to a gradual salinity change (GSC) by increasing FW’s salinity to SW. The gradient was set at 3 salinity points, changing 10 PSU per week for a month. Intestine samples were taken after a week of acclimation in each salinity point. Meanwhile, another group of 30 smolts per tank in triplicate was exposed to a salinity shock (SS) and a transfer from FW to 32 PSU on the same day as the GSC group. These two groups were fed a regular diet of Cargill. The third group of 30 smolts per tank in triplicate was fed for a month with a functional diet (FD) of SuperSmolt Feed Only, Stim company (unsolicited study), and transferred to 32 PSU at the same time as the other groups. Fish intestine samples of each group were taken after a week of acclimation at 32 PSU. Furthermore, the salmon condition to SW transfer was evaluated by immune histochemistry analyses performed by the VEHICE company, Chile. In addition, RT-qPCR expression analysis of ATPase-α and ATPase-β was determined using the comparative ΔΔCt relative expression analysis. The primers and qPCR conditions were similar to those previously described for our group [33]. Animal procedures were carried out under the guidelines approved by the Ethics Committee of the University of Concepción. The experimental design considered the Three Rs (3Rs) guidelines for animal testing.

2.2. DNA Extraction and Full-16S rRNA Amplification

After the fish intestine digest was removed, intestinal tissues were thoroughly minced and then mixed with 1 mL of lysis buffer (10 mM Tris-HCl, 400 mM NaCl, 100 mM EDTA, 0.4% SDS, and 5 µL of 20 mg/mL Protease K, pH 8.0), after which they were thoroughly vortexed and incubated for 2 h at 37 °C. The samples were homogenized for 5 min at 24 Hz in an oscillating mill (MM200, Retsch) using 1.4 mm ceramic spheres, followed by the phenol:chloroform:isoamyl method. DNA integrity was assessed by 1% agarose gel electrophoresis after extraction. The DNA concentration was measured with a Nanodrop spectrophotometer. Five individuals per experimental group were pooled in a final concentration of 100 ng/µL. The full-16S rRNA gene was amplified using the primers 27 F 5′-AGAGTTTGATCCTGGCTCAG-3′ and 1492 R 5′-GGTTACCTTGTTACGACTT-3′ [34]. Fifteen µL Taq DNA polymerase LongAmp (New England Biolabs, Ipswich, MA, USA) was used for amplification, under the following conditions: 95 °C for 1 min, followed by 25 cycles of 95 °C, 56 °C for 30 sec, and 65 °C for 1 min, with a final extension at 65 °C for 5 min. Electrophoresis in agarose gel at 1.2% was used to assess PCR results.

2.3. Nanopore Library Synthesis and Sequencing

For Nanopore, the library was conducted in triplicate per each experimental group, using a full 16S rRNA PCR product of a pool of five individuals. The PCR products were purified in a ratio of 1:2 sample:beads using Agencourt AMPure XP beads (Beckman Coulter, Brea, CA, USA). The samples were placed in the magnetic stand for washing with 70% ethanol (freshly prepared). The beads were resuspended with molecular biology-grade water. The purified amplicon was quantified in the Qubit 4 fluorometer (Thermo Scientific, Waltham, MA, USA) and used as a template for library synthesis with the 16S Barcoding Kit (SQK-RAB204, Oxford Nanopore Technologies), following the manufacturer’s instructions for the 1D sequencing strategy. Briefly, a purified 16S amplicon was mixed with barcodes, and a PCR was done as described in the preceding stage, with a final reaction volume of 50 uL, using the LongAmp Taq Polymerase (New England Biolabs). The PCR product was incubated for 5 min at room temperature in a HulaMixer (Thermo Scientific) and cleaned with Agencourt AMPure XP beads. The purified product was eluted in 10 uL of elution buffer (10 mM Tris-HCl pH8.0 with 50 mM NaCl). The final concentration of the library was measured using a Qubit 4 fluorometer (Thermo Scientific), and libraries were tested using High Sensitivity D5000 ScreenTape (Agilent, Santa Clara, CA, USA), according to the manufacturer’s instructions, on a TapeStation Bioanalyzer 2100 (Agilent). Following Oxford Nanopore Technologies’ methodology, the libraries were pooled in multiplex mode and sequencing into the flowcell MK1 Spot-ON FLO-MIN107-R9. As an internal control, the DNA of a microbial mock community (Zymo Biomics Microbial Community Standard) was extracted and sequenced following the same described procedures, and the observed abundances of taxa were compared with their expected abundance. Sequencing efficiency was monitored through the software MinKNOW 2.0 (Oxford Nanopore Technologies).

2.4. Bioinformatic Analysis

The fast5 files generated were base-called using Guppy (version 3.2.2, Oxford Nanopore Technologies, Oxford, UK), and a filter step was applied to retain only sequences with a Q-score ≥ 7 (quality filter). The demultiplexing, primers, and barcode trimming was done with Porechop V0.2.4 [35]. BLASTN aligned cleaned sequences 16S NCBI taxonomy database in the NanoCLUST pipeline [36]. This included filtering by sequence size 1400–1800 bp and Q-score ≥ 9. Simpson’s 1-D and Shannon index were used to estimate alpha diversity, while Pielou’s index was used to estimate evenness. Microbial community structure was analyzed using Bray-Curtis dissimilarity based on taxon relative abundance data, and principal coordinate analysis (PCoA) was performed as a multivariate unsupervised data exploration. All indexes and PCoA were calculated using R’s “Vegan” package [37]. Variations of the intestinal microbiome were explored by plotting the relative abundance of phyla, orders, and genera in R statistical software [38]. PICRUSt2 software was used to predict metagenome function using the V3–V4 region obtained from the full16S rRNA sequences [39]. These regions were identified by an alignment between our sequencing data with universal primers [26] for V3–V4 in CLC program. The pathway levels were built using the MetaCyc database [40]. A relative abundance plot was generated using R. We used the STAMP 2.1.3 program to test for significant differences in pathway contributions [41]. A chi-square test corrected by Benjamini–Hochberg’s false discovery rate was applied. For graph building, data was used with a minimum relative abundance of 0.5 to determine proportion difference.

3. Results

3.1. Experimental Performance of Atlantic Salmon

Chloride cell movement was seen in the immune histochemistry analysis of Atlantic salmon subjected to the GSC, SS, and FD conditions, showing that the conditions were suitable for SW transfer (Figure S2). Additionally, RT-qPCR examination of ATPase-α and ATPase-β subunits validated this situation (Figure S3). In experimental groups, mortality was not observed.

3.2. Full-16S Sequencing Data Report

The Nanopore sequencing generated 5,867,910 reads filtered by Guppy and then processed for secondary metagenomic analysis. After demultiplexing, trimming, quality, and size-filtering, 46.18% of the reads were classified by NanoCLUST. A total of 96,160 reads were classified taxonomically, including the mock community, with a mean of 13,308 per condition. All non-classified bacteria were eliminated from the study; only classified taxa were included in the diversity and taxonomic studies (Tables S1 and S2).

3.3. Structure of The Intestinal Microbial Community

The rarefaction curves indicated that all samples reached the plateau, which means that the number of sequences was sufficient for taxonomic classification. However, only groups 10PSU-GSC and 20PSU-GSC had more than 10,000 reads (Figure S4). The Bray-Curtis dissimilarities for fish intestinal microbiota for all groups show values between 0.67–0.65. The transfer from FW to SW, including the gradient, shows a high discrepancy (0.68–0.91). The highest dissimilarity is observed at the first salinity change (10PSU-GSC: 0.91). Focusing only on the change from FW to 32PSU, we observe that 32PSU-GSC (0.67) presents the most minor dissimilarity, while 32PSU-SS and 32PSU-FD show a similar dissimilarity (0.88–0.85). Generally, the lowest dissimilarity was between the GSC groups (10PSU-GSC, 20PSU-GSC) and the groups 32PSU-SS and 32PSU-FD (Table S3). The principal coordinate analysis (PCoA) using the Bray–Curtis dissimilarity showed four clusters. One grouped the 10PSU-GSC and 20PSU-GSC (Figure 1A). A second cluster grouped the 32PSU-SS and 32PSU-FD fish samples. The third cluster grouped the FW samples, and the fourth cluster consisted of the 32PSU-GSC independently distributed. The highest bacteria diversity was observed in individuals from group 10PSU-GSC, according to the Simpson (1-D) and Shannon indexes (Figure 1B,C), while the group with the least distribution was the FW. According to Pielou’s index, the group with the least uniformity was the intestinal fish at 20PSU-GSC (Figure 1D). Related to the samples obtained after one week in SW, the Simpson’s and Shannon’s indexes showed high bacterial diversity in fish from 32PSU-FD (Figure 1B,C). On the other hand, Pielou’s index showed more uniformity in group 32PSU-SS (Figure 1D).

3.4. Atlantic Salmon Intestine Microbiota Composition during The SW Transfer

All experimental groups identified 10 phyla in the intestinal microbiota (Figure 2A), and 89% of the microbiota were identified in Proteobacteria phylum. Additionally, the Bacteroidetes, Firmicutes, and Actinobacteria phyla were highly abundant in the microbiota sample. Intestine samples from FW were the only ones with the presence of Armatimonadetes. In contrast, the intestine microbiota from the 10PSU-GSC group had the presence of Acidobacteria, Fusobacteria, and Verrucomicobia (Figure 2A), whereas the phylum Cyanobacteria was distinguished in the intestinal microbiota of the 20PSU-GSC group. Moreover, the intestine microbiota of the 32PSU-SS group only exhibited bacteria of the phyla Proteobacteria and Bacterioidetes. Finally, the presence of Thermotogae phylum in the microbiota of the 32PSU-FD group was notable (Figure 2A).
The microbiota relative abundance of the top 25 genera showed a dominance of the genus Escherichia-Shigella (Enterobacterales) in all analyzed samples, except for the 10 PSU-GSC group. For this group, the specie distribution was more homogenous (Figure 2B). Notably, the intestine microbiota in the FW, 10 PSU, and 20 PSU samples exhibited more bacterial genera diversity than intestine microbiota at 32 PSU. Interestingly, the microbiota of samples of all groups at 32 PSU exhibited the presence of the genus Vibrio, with the highest abundance in the 32 PSU-SS group (Figure 2B).
Finally, a core microbiota was observed among all experimental groups. This core was composed of the orders Flavobacteriales, Enterobacterales, Moraxellales, and Pseudomonadales (Figure 3A). The analysis by genus reveals that the genus Escherichia-Shigella was the most abundant in the intestine core microbiota, followed by the genera Acinetobacter and Pseudomonas (Figure 3B).

3.5. Bacteria Species Identified in the Intestinal Atlantic Salmon Microbiota

Seventy clusters of species generated by NanoCLUST were above a threshold of the 98.7% of identity defined by Yarza et al. [14], equivalent to only 17.7% of the total clusters. The Acinetobacter johnsonii is the only specie that was identified in the intestinal microbiota of all experimental groups (Table S4). In addition, species were observed that were presented in FW and maintained in the intestine microbiota of fish exposed to the gradual salinity change, such as Pseudomonas migulae and Shigella flexneri. Furthermore, the intestine microbiota of 32PSU-GSC contained species such as Aliivibrio wodanis, Methylobacterium brachiatum, Microbacterium mangrove, Micrococcus luteus, and Sphingobium yanoikuyae.
Through the NanoCLUST analysis, 46 clusters of potentially pathogenic bacteria were classified. However, only 5 represent an average identity and relative abundance above 98.7% and 0.2, respectively (Table S4). These clusters of pathogenic groups identified in all data sets were the species Acinetobacter johnsonii, Aliivibrio wodanis, Flavobacterium succinicans, and Providencia rettgeri. Interestingly, the Acinetobacter johnsonii specie was present in the intestinal microbiota of all the experimental fish groups (Table S4).

3.6. Intestine Microbiota after Seawater Transfer

In addition, the microbiota abundance and richness among fish groups after a week in seawater were evaluated. The phylum Proteobacteria was the most abundant in the intestine microbiota for each experimental fish group. Furthermore, this phylum exhibited the highest richness at the genus level. In particular, the genera Vibrio, Pseudomonas, Escherichia-Shigella, and Acinetobacter were present in the microbiota at 32PSU in all groups (Figure 4). The intestinal microbiota of the 32PSU-GSC group showed more richness of the phylum Firmicutes, especially the Bacillales and Lactobacillales genera. In addition, the 32PSU-SS group exhibited the highest abundance of the Vibrio genus, reaching 45%. The 32PSU-FD group showed more abundance and richness of the genera of the phylum Bacteroidetes. In addition, this group exhibited high richness of the phylum Proteobacteria, mainly the genus Ralstonia and Pelomonas, compared with the other groups at 32PSU (Figure 4). Finally, the 32PSU-FD group is the only one with the presence of the genus Thermotogae in its microbiota.

3.7. Functional Analysis in the Intestinal Atlantic Salmon Microbiota

We identified 338 functional pathways in the Atlantic salmon intestine microbiota with PICRUSt2 software [39]. Forty-eight of them were of level 2, and the majority are related to biosynthesis (Figure 5A, Table S5). Pathways with an effect size > 0.5 and p < 0.05 among the salinity conditions were obtained by STAMP to compare the different SW treatments (Figure 5B–D). The most abundant pathways were associated with Biosynthesis of Vitamins, Amino Acids, Nucleoside and Nucleotide, Fatty acid, and Lipid (Figure 5A). The 5 pathways more abundant in the FW group were annotated at the level 2 descriptions Secondary Metabolite Degradation, Citrate cycle (TCA cycle), C1 Compound Utilization and Assimilation, and Nucleoside and Nucleotide Biosynthesis. Under the top 5 pathways more abundant in the 32 PSU-GSC group, TCA cycle was identified as a level 2 description. For the group 32 PSU-SS, Secondary Metabolic Degradation and TCA cycle were more abundant at the level 2 description, while the level 2 descriptions found with more abundance in the 32 PSU-FD group were Secondary Metabolite Degradation, Nucleoside and Nucleotide Biosynthesis, and TCA cycle (Table S5).
In addition, the comparison among the FW and SW samples showed similar pathways. Notably, compared with SW, the FW metagenome showed a higher abundance of TCA cycle, Fatty Acid and Lipid Biosynthesis, Nucleoside and Nucleotide Biosynthesis, and Amino Acid Biosynthesis. The functional analysis revealed a significant difference in the metagenomics potential among the samples at 32 PSU. For instance, between 32 PSU-GSC and 32 PSU-SS, Aromatic Compound Degradation and TCA cycle were significantly higher in the 32 PSU-GSC group (Figure 5B). From the comparative analysis of 32 PSU-GSC and 32 PSU-FD, 12 pathways showed a difference in abundance, highlighting pathways such as Amino Acid Biosynthesis, Fatty Acid and Lipid Biosynthesis, and Amino Acid degradation, which exhibited high abundance in the 32 PSU-FD group (Figure 5C).

4. Discussion

Fish microbiota play a relevant role in the salmon’s performance and can be influenced by the diet, fish physiology, and environment, among other factors. During smoltification, Atlantic salmon are exposed to environmental change from freshwater (FW) to seawater [42]. Thus, their microbiota diversity can be modified and affect the seawater fish performance. Here, we used the full 16S rRNA sequencing to evaluate the Atlantic salmon intestinal microbiota variation during the SW transfer under different strategies. It was explored if a fish transfer to SW by gradual salinity change (GSC) exhibited differences in microbiota abundance and diversity compared with fish exposed to salinity shock (SS), as it is performed in the industry.
A total of 19 OTUs have been reported in the core intestine microbiota between FW and SW Atlantic salmon [20]. Among these OTUs, the authors reported the presence of Lactobacillus, Lactococus, Streptococcus, Escherichia/Shigella, Pseudomonas, and Mycoplasma. Moreover, Dehler et al. [26] reported Escherichia/Shigella in the core microbiota of Atlantic salmon pre-smolts in FW in aquarium and loch environment conditions. In addition, Lorgen-Ritchie et al. [9] describe the presence of Pseudomonas sp. in the core microbiota of FW/SW Atlantic salmon gut. Interestingly, this study identified a microbial core composed of Pseudomonas, Escherichia/Shigella, and Acinetobacter. The presence of Acinetobacter bacteria in Atlantic salmon gut microbiota has not been described previously. However, in FW Atlantic salmon, skin microbiota has been reported to have a high abundance of Acinetobacter [8]. It is suggested that the low diversity found in the intestine core microbiota is due to the study being carried out under laboratory conditions that can reduce the environmental microbiota.
Previously, the high species richness of Atlantic salmon gut microbiota in sea cages compared with FW gut microbiota has been reported [10]. Furthermore, increased bacteria diversity has been reported in the FW gut microbiota of Atlantic salmon in a RAS system compared with salmon gut microbiota transfer to SW [9]. In this study, the bacteria diversity analysis showed that the salmon intestinal microbiota of the 10PSU-GSC group exhibited the highest bacteria diversity among the intestine samples evaluated. Thus, this suggests that the gradual adaptation of salmon from FW to 10PSU-GSC favors the intestinal microbiota diversity in pre-smolts. Interestingly, among the intestine samples evaluated after a week in seawater, the Atlantic salmon microbiota exposed to GCS and the group feeding with the FD exhibited greater bacteria diversity than the group transferred to SW by salinity shock. Notably, the transcriptome analysis of the Atlantic salmon transferred to SW by gradual salinity change reported an expression increase of immune-related genes compared with salmon exposed to salinity shock [33]. Thus, it is possible to suggest that the increase of microbiota diversity in fish exposed to GSC can be associated with healthy fish. In general, low diversity in the intestinal microbiota is a marker of dysbiosis and has been associated with a wide range of diseases in humans [43]. Now, in fish, diseased-looking tilapia (ocular exophthalmos, skin hemorrhages, skin lesions, and necrosis) have been found to have a lower diversity index than healthy fish [44].
Among the phyla presented in the Atlantic salmon intestine microbiota, previous studies have reported a freshwater predominance of the phyla Proteobacteria and Firmicutes [9,10,21]. Additionally, high dominance of the Proteobacteria phylum has been reported in seawater [9]. Moreover, an increased presence of Firmicutes has been observed in the Atlantic salmon intestine after 20 weeks in SW [10]. Moreover, the phylum Proteobacteria has demonstrated an abundance decrease after eight months in seawater [10]. In this study, the phylum Proteobacteria was the most abundant in all the evaluated intestine samples. Among the treatments, Firmicutes and Bacteroidetes phyla were more abundant in the intestines of fish exposed to 10 and 20 PSU. Moreover, the Firmicutes phylum has been described in the gut core microbiota of Atlantic salmon identified between FW and SW [26]. Here, the GSC group’s intestine microbiota exhibited Firmicutes from FW to all salinity points. In addition, the intestine microbiota of the FD group presented the Firmicutes phylum. Thus, this suggests that the FD and the GSC stimulate the establishment of Firmicutes. Furthermore, the use of functional ingredients in salmon farming, such as insect meal, galactomannan oligosaccharides, and prebiotics, increases the Firmicutes abundance [3,10]. Notably, the Firmicutes phylum is not presented in the intestine microbiota of fish exposed to saline shock. Similarly, in wild salmon, the Firmicutes phylum is observed in stages associated with the FW, such as parr, smolts, and returning adults [45]. The gradual salinity change and the functional diet allow the presence of the Firmicutes phylum.
Vibrio genus was identified in the Atlantic salmon intestine microbiota after a week at 32 PSU, mainly in fish exposed to the salinity shock. Species of this genus are abundant in marine ecosystems [46,47]. For instance, Vibrio species have been reported in the intestines of shrimp, mollusks, abalones, and others [47]. Furthermore, the genus Vibrio is associated with pathogenicity in fish [48]. Additionally, after four weeks of SW transfer, the presence of the Vibrionaceae family in the gut microbiota of Atlantic salmon smolts has been reported [9]. Moreover, comparative study of the gut microbiota of Atlantic salmon in a control aquarium vs. a loch environment has indicated the presence of Aliivibrio in the core microbiota [20].
Notably, the genus Lactobacillus has been reported in greater abundance in Atlantic salmon intestine microbiota [9,10,26]. Moreover, the presence of Lactobacillus has been reported in the intestinal core microbiota of Atlantic salmon in FW and SW [26]. In addition, in a RAS system, the Lactobacillus species was identified among Atlantic salmon’s FW gut core microbiota [9]. In this study, the intestinal microbiota analyzed exhibited the absence of the genus Lactobacillus. However, Streptococcus thermophilus, from the Lactobacillales order, was identified in the intestine microbiota of 32 PSU-GSC. We hypothesize that the absence of the Lactobacillus genus in our study can be a consequence of the DNA extraction method used [49]. Another explanation can be associated with the Taq Polymerase used for the 16S library preparation, which may not favor the detection of this genus [50].
An advantage of using the complete 16S rRNA sequencing by Nanopore sequencing is the possibility to infer the microbiota metagenome. In this study, we used the V3–V4 region from 16S to perform functional analysis. However, the intestinal Atlantic salmon microbiota in this study showed some differences compared with other studies. For instance, in the FW microbiota of salmon, a high proportion of function associated with Carbohydrate Metabolisms, TCA cycle, Lipid Biosynthesis, Fatty Acid Biosynthesis, and oxidative phosphorylation has been reported [26]. However, in SW, fish microbiota exhibited a high enrichment of pathways such as Carbohydrate Metabolism, Amino Sugar and Nucleotide Sugar Metabolism, and Glycolysis/Gluconeogenesis. Additionally, differences in the metabolic processes of Atlantic salmon gut microbiota in FW and SW were reported by Lorgen-Ritchie et al. [9]. In this study, the intestine microbiota from SW groups exhibited a high relative abundance of pathways associated with Carbohydrate Degradation, Cell Structure, and Secondary Metabolite Degradation. Notably, in our study, the metagenomic analysis of FW and SW microbiota exhibited a high abundance of TCA cycle, Fatty Acid and Lipid Biosynthesis, Nucleoside and Nucleotide Biosynthesis, and Amino Acid Biosynthesis. In general, Amino Acid Biosynthesis stands out in metagenomic functional studies on intestinal fish [51]. Furthermore, valine, leucine, and isoleucine are essential metabolites for fish [52]. The 32 PSU-FD fish intestinal microbiota exhibited the highest enrichment of Amino Acid Biosynthesis. Contrary to our supposition, 32PSU-SS fish microbiota ranks second. However, focusing on the essential amino acid degradation pathway is more favored in the FD and SS treatments over GSC. Aromatic Compound Degradation is the pathway with the most significant differences between treatments. Aromatic amino acids, plant constituents, drugs, additives, colorants, and contaminants are some of the sources of aromatic compounds in the intestine [53]. Therefore, FD and GSC may have an advantage over SS in using aromatic compounds as a carbon source and eliminating toxins from the bacteria found in the fish intestine.
Concerning the findings archived during the study for the in-feed functional ingredients, there is strong evidence of the association of functional ingredients, such as essential fatty acids, nucleotides, yeast cell walls, and prebiotics, in the intestine fish microbiota modulation [10,54]. For instance, a high abundance of Proteobacteria and Mycoplasmas has been observed in Atlantic salmon feeding with functional ingredients after 44 weeks in seawater, compared with salmon feeding with a regular diet [10]. Moreover, a high difference in the microbiota diversity of sea bass (Dicentrarchus Labrax) feeding with functional ingredients (FI) has been reported [54]. Furthermore, sea bass feeding with FI reduces potentially pathogenic bacteria, such as Vibrionales [54]. Notably, the results obtained in the current study revealed that fish feeding with FD exhibited a higher bacteria genus richness than the other experimental groups. Furthermore, Atlantic salmon feeding with FD at 32 PSU showed a low abundance of Vibrio genus compared with the other experimental groups. Thus, besides functional ingredients improving the fish immune system, it also impacts the fish microbiota abundance and richness.
Our results show the potentiality of salmon microbiota studies to determine the smolt condition. It was demonstrated that the gradual salinity change increases the salmon microbiota abundance, thus improving their health. The implementation of an Atlantic salmon transfer by gradual exposure to seawater could increase the transfer’s success. Nowadays, the salmon industry has been increasing the time of fish in the RAS conditions before transferring to seawater as a strategy to reduce the exposure to sea pathogens [55]. Thus, the industry could implement the gradual salinity change in RAS systems, improving salmon performance in seawater.

5. Conclusions

The differences in the diversity indices demonstrate variation in the intestinal microbiota of Atlantic salmon during the transfer from FW to SW. The richness and diversity indices were more significant in the intestinal microbiota of Atlantic salmon exposed to a gradual salinity change. Proteobacteria were dominant in all groups, but there were variations in lower taxonomic levels in all conditions. Escherichia/Shigella were found in high abundance as part of SW microbiota. Despite the taxonomic differences found among treatments, a low percentage of the metabolic pathways analyzed showed significant differences; most of them are related to biosynthesis. Finally, this is the first study that evaluates the intestinal microbiota of Atlantic salmon exposed to gradual salinity change during smoltification, and it shows that this way of transferring to SW increases the diversity of the microbiota of the fish and, thus, improves their health condition.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/microorganisms11010076/s1; Figure S1: Experimental design; Figure S2: Localization of chloride cells in the gill filament epithelium; Figure S3: RT-qPCR analysis of ATPase-α and ATPase-β subunits; Figure S4: Rarefaction curve; Figure S5: Mock community composition; Table S1: Sequencing data report; Table S2: Complete NanoCLUST classification cluster; Table S3: Bray-Curtis similarities for intestine samples calculated on R with Vegan Package; Table S4: NanoCLUST average percent identity of Clusters at the species level. Species with percentage of identity ≥ 98.7 based on the full sequence of 16S rRNA gene and relative abundance ≥ 0.2%; Table S5: Complete metabolic MetaCyc pathway abundance of freshwater (FW) and different seawater treatment inferred by PICRUSt2.

Author Contributions

Conceptualization, M.F.M.-R., D.V.-M., G.N.-A., and V.V.-M.; Data curation, M.F.M.-R.; Formal analysis, M.F.M.-R.; Funding acquisition, D.V.-M., C.G.-E., and V.V.-M.; Investigation, M.F.M.-R., B.P.B., and V.V.-M.; Methodology, M.F.M.-R., D.V.-M., G.N.-A., B.P.B., C.G.-E., and V.V.-M.; Project administration, V.V.-M.; Resources, C.G.-E.; Supervision, C.G.-E. and V.V.-M.; Visualization, M.F.M.-R.; Writing—original draft, M.F.M.-R. and V.V.-M.; Writing—review & editing, D.V.-M., G.N.-A., C.G.-E., and V.V.-M. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by ANID-Chile through the Postdoctoral grant FONDECYT (3190320), grants FONDAP (15110027), FONDECYT (1210852), FONDECYT (11220307), Postdoctoral grant FONDECYT (3200600).

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Egerton, S.; Culloty, S.; Whooley, J.; Stanton, C.; Ross, R.P. The Gut Microbiota of Marine Fish. Front. Microbiol. 2018, 9, 873. [Google Scholar] [CrossRef] [PubMed]
  2. Schmidt, V.T.; Smith, K.F.; Melvin, D.W.; Amaral-Zettler, L.A. Community assembly of a euryhaline fish microbiome during salinity acclimation. Mol. Ecol. 2015, 24, 2537–2550. [Google Scholar] [CrossRef] [PubMed]
  3. Li, Y.; Bruni, L.; Jaramillo-Torres, A.; Gajardo, K.; Kortner, T.M.; Krogdahl, A. Differential response of digesta- and mucosa-associated intestinal microbiota to dietary insect meal during the seawater phase of Atlantic salmon. Anim. Microbiome 2021, 3, 8. [Google Scholar] [CrossRef]
  4. Harrison, B.K.; Myrbo, A.; Flood, B.E.; Bailey, J.V. Abrupt burial imparts persistent changes to the bacterial diversity of turbidite-associated sediment profiles. Geobiology 2018, 16, 190–202. [Google Scholar] [CrossRef] [PubMed]
  5. Labonte, J.M.; Lever, M.A.; Edwards, K.J.; Orcutt, B.N. Influence of Igneous Basement on Deep Sediment Microbial Diversity on the Eastern Juan de Fuca Ridge Flank. Front. Microbiol. 2017, 8, 1434. [Google Scholar] [CrossRef] [Green Version]
  6. Mills, H.J.; Reese, B.K.; Shepard, A.K.; Riedinger, N.; Dowd, S.E.; Morono, Y.; Inagaki, F. Characterization of Metabolically Active Bacterial Populations in Subseafloor Nankai Trough Sediments above, within, and below the Sulfate-Methane Transition Zone. Front. Microbiol. 2012, 3, 113. [Google Scholar] [CrossRef] [Green Version]
  7. Rud, I.; Kolarevic, J.; Holan, A.B.; Berget, I.; Calabrese, S.; Terjesen, B.F. Deep-sequencing of the bacterial microbiota in commercial-scale recirculating and semi-closed aquaculture systems for Atlantic salmon post-smolt production. Aquac. Eng. 2017, 78, 50–62. [Google Scholar] [CrossRef]
  8. Lokesh, J.; Kiron, V. Transition from freshwater to seawater reshapes the skin-associated microbiota of Atlantic salmon. Sci. Rep. 2016, 6, 19707. [Google Scholar] [CrossRef] [Green Version]
  9. Lorgen-Ritchie, M.; Clarkson, M.; Chalmers, L.; Taylor, J.F.; Migaud, H.; Martin, S.A.M. A Temporally Dynamic Gut Microbiome in Atlantic Salmon During Freshwater Recirculating Aquaculture System (RAS) Production and Post-seawater Transfer. Front. Mar. Sci. 2021, 8, 711797. [Google Scholar] [CrossRef]
  10. Wang, J.; Jaramillo-Torres, A.; Li, Y.; Kortner, T.M.; Gajardo, K.; Brevik, O.J.; Jakobsen, J.V.; Krogdahl, A. Microbiota in intestinal digesta of Atlantic salmon (Salmo salar), observed from late freshwater stage until one year in seawater, and effects of functional ingredients: A case study from a commercial sized research site in the Arctic region. Anim. Microbiome 2021, 3, 14. [Google Scholar] [CrossRef]
  11. Bukin, Y.S.; Galachyants, Y.P.; Morozov, I.V.; Bukin, S.V.; Zakharenko, A.S.; Zemskaya, T.I. The effect of 16S rRNA region choice on bacterial community metabarcoding results. Sci. Data 2019, 6, 190007. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  12. Kerrigan, Z.; Kirkpatrick, J.B.; D'Hondt, S. Influence of 16S rRNA Hypervariable Region on Estimates of Bacterial Diversity and Community Composition in Seawater and Marine Sediment. Front. Microbiol. 2019, 10, 1640. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  13. Willis, C.; Desai, D.; LaRoche, J. Influence of 16S rRNA variable region on perceived diversity of marine microbial communities of the Northern North Atlantic. Fems Microbiol. Lett. 2019, 366, fnz152. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  14. Yarza, P.; Yilmaz, P.; Pruesse, E.; Glockner, F.O.; Ludwig, W.; Schleifer, K.H.; Whitman, W.B.; Euzeby, J.; Amann, R.; Rossello-Mora, R. Uniting the classification of cultured and uncultured bacteria and archaea using 16S rRNA gene sequences. Nat. Rev. Microbiol. 2014, 12, 635–645. [Google Scholar] [CrossRef]
  15. Matsuo, Y.; Komiya, S.; Yasumizu, Y.; Yasuoka, Y.; Mizushima, K.; Takagi, T.; Kryukov, K.; Fukuda, A.; Morimoto, Y.; Naito, Y.; et al. Full-length 16S rRNA gene amplicon analysis of human gut microbiota using MinION nanopore sequencing confers species-level resolution. BMC Microbiol. 2021, 21, 35. [Google Scholar] [CrossRef]
  16. Fujiyoshi, S.; Muto-Fujita, A.; Maruyama, F. Evaluation of PCR conditions for characterizing bacterial communities with full-length 16S rRNA genes using a portable nanopore sequencer. Sci. Rep. 2020, 10, 12580. [Google Scholar] [CrossRef]
  17. Johnson, J.S.; Spakowicz, D.J.; Hong, B.Y.; Petersen, L.M.; Demkowicz, P.; Chen, L.; Leopold, S.R.; Hanson, B.M.; Agresta, H.O.; Gerstein, M.; et al. Evaluation of 16S rRNA gene sequencing for species and strain-level microbiome analysis. Nat. Commun. 2019, 10, 5029. [Google Scholar] [CrossRef] [Green Version]
  18. Shin, J.; Lee, S.; Go, M.J.; Lee, S.Y.; Kim, S.C.; Lee, C.H.; Cho, B.K. Analysis of the mouse gut microbiome using full-length 16S rRNA amplicon sequencing. Sci. Rep. 2016, 6, 29681. [Google Scholar] [CrossRef] [Green Version]
  19. Cusco, A.; Catozzi, C.; Vines, J.; Sanchez, A.; Francino, O. Microbiota profiling with long amplicons using Nanopore sequencing: Full-length 16S rRNA gene and the 16S-ITS-23S of the rrn operon. F1000Res 2018, 7, 1755. [Google Scholar] [CrossRef]
  20. Dehler, C.E.; Secombes, C.J.; Martin, S.A. Environmental and physiological factors shape the gut microbiota of Atlantic salmon parr (Salmo salar L.). Aquaculture 2017, 467, 149–157. [Google Scholar] [CrossRef]
  21. Skrodenyte-Arbaciauskiene, V.; Virbickas, T.; Luksa, J.; Serviene, E.; Blazyte-Cereskiene, L.; Kesminas, V. Gut Microbiome of Wild Baltic Salmon (Salmo salar L.) Parr. Microb. Ecol. 2022, 84, 1294–1298. [Google Scholar] [CrossRef] [PubMed]
  22. Sprockett, D.; Fukami, T.; Relman, D.A. Role of priority effects in the early-life assembly of the gut microbiota. Nat. Rev. Gastroenterol. Hepatol. 2018, 15, 197–205. [Google Scholar] [CrossRef] [PubMed]
  23. Dulski, T.; Kujawa, R.; Godzieba, M.; Ciesielski, S. Effect of Salinity on the Gut Microbiome of Pike Fry (Esox lucius). Appl. Sci. 2020, 10, 2506. [Google Scholar] [CrossRef] [Green Version]
  24. Wu, P.; Liu, Y.; Li, C.; Xiao, Y.; Wang, T.; Lin, L.; Xie, Y. The Composition of Intestinal Microbiota From Collichthys lucidus and Its Interaction With Microbiota From Waters Along the Pearl River Estuary in China. Front. Environ. Sci. 2021, 9, 675856. [Google Scholar] [CrossRef]
  25. Sundh, H.; Nilsen, T.O.; Lindstrom, J.; Hasselberg-Frank, L.; Stefansson, S.O.; McCormick, S.D.; Sundell, K. Development of intestinal ion-transporting mechanisms during smoltification and seawater acclimation in Atlantic salmon Salmo salar. J. Fish Biol. 2014, 85, 1227–1252. [Google Scholar] [CrossRef]
  26. Dehler, C.E.; Secombes, C.J.; Martin, S.A.M. Seawater transfer alters the intestinal microbiota profiles of Atlantic salmon (Salmo salar L.). Sci. Rep. 2017, 7, 13877. [Google Scholar] [CrossRef] [Green Version]
  27. Milligan-Myhre, K.; Small, C.M.; Mittge, E.K.; Agarwal, M.; Currey, M.; Cresko, W.A.; Guillemin, K. Innate immune responses to gut microbiota differ between oceanic and freshwater threespine stickleback populations. Dis. Model Mech. 2016, 9, 187–198. [Google Scholar] [CrossRef] [Green Version]
  28. Sernapesca. Informe Sanitario con Informacion Sanitaria de Agua Dulce y Mar Año 2021; Departamento de Salud Animal, Subdirección de Acuicultura, Gobierno de Chile: Santiago, Chile, 2021. [Google Scholar]
  29. Nisembaum, L.G.; Martin, P.; Lecomte, F.; Falcon, J. Melatonin and osmoregulation in fish: A focus on Atlantic salmon Salmo salar smoltification. J. Neuroendocrinol. 2021, 33, e12955. [Google Scholar] [CrossRef]
  30. Folmar, L.C.; Dickhoff, W.W. The parr-smolt transformation (smotification) and seawater adaptation in salmonids. A review of selected literature. Aquaculture 1980, 21, 1–37. [Google Scholar] [CrossRef]
  31. Johansson, L.H.; Timmerhaus, G.; Afanasyev, S.; Jorgensen, S.M.; Krasnov, A. Smoltification and seawater transfer of Atlantic salmon (Salmo salar L.) is associated with systemic repression of the immune transcriptome. Fish Shellfish Immunol. 2016, 58, 33–41. [Google Scholar] [CrossRef]
  32. Sahlmann, C.; Djordjevic, B.; Lagos, L.; Mydland, L.T.; Morales-Lange, B.; Øvrum Hansen, J.; Ånestad, R.; Mercado, L.; Bjelanovic, M.; Press, C.M.; et al. Yeast as a protein source during smoltification of Atlantic salmon (Salmo salar L.), enhances performance and modulates health. Aquaculture 2019, 513, 734396. [Google Scholar] [CrossRef]
  33. Valenzuela-Muñoz, V.; Gallardo-Escarate, C.; Benavente, B.P.; Valenzuela-Miranda, D.; Nunez-Acuna, G.; Escobar-Sepulveda, H.; Valdes, J.A. Whole-Genome Transcript Expression Profiling Reveals Novel Insights into Transposon Genes and Non-Coding RNAs during Atlantic Salmon Seawater Adaptation. Biology 2021, 11, 1. [Google Scholar] [CrossRef] [PubMed]
  34. Lane, D.J. 16S/23S rRNA sequencing. In Nucleic Acid Techniques in Bacterial Systematics; Stackebrandt, E., Goodfellow, M., Eds.; Wiley: Hoboken, NJ, USA, 1991; Volume 4, pp. 115–175. [Google Scholar]
  35. Wick, R. Porechop: An adapter trimmer for Oxford Nanopore reads. 2018. Available online: https://github.com/rrwick/Porechop (accessed on 15 July 2022).
  36. Rodriguez-Perez, H.; Ciuffreda, L.; Flores, C. NanoCLUST: A species-level analysis of 16S rRNA nanopore sequencing data. Bioinformatics 2021, 37, 1600–1601. [Google Scholar] [CrossRef] [PubMed]
  37. Dixon, P. VEGAN, a package of R functions for community ecology. J. Veg. Sci. 2003, 14, 927–930. [Google Scholar] [CrossRef]
  38. R-Core-Team. R: A Language and Environment for Statistical Computing; R Foundation for Statistical Computing: Vienna, Austria, 2020. [Google Scholar]
  39. Douglas, G.M.; Maffei, V.J.; Zaneveld, J.R.; Yurgel, S.N.; Brown, J.R.; Taylor, C.M.; Huttenhower, C.; Langille, M.G.I. PICRUSt2 for prediction of metagenome functions. Nat. Biotechnol. 2020, 38, 685–688. [Google Scholar] [CrossRef]
  40. Caspi, R.; Billington, R.; Fulcher, C.A.; Keseler, I.M.; Kothari, A.; Krummenacker, M.; Latendresse, M.; Midford, P.E.; Ong, Q.; Ong, W.K.; et al. The MetaCyc database of metabolic pathways and enzymes. Nucleic Acids Res. 2018, 46, D633–D639. [Google Scholar] [CrossRef] [Green Version]
  41. Parks, D.H.; Tyson, G.W.; Hugenholtz, P.; Beiko, R.G. STAMP: Statistical analysis of taxonomic and functional profiles. Bioinformatics 2014, 30, 3123–3124. [Google Scholar] [CrossRef] [Green Version]
  42. Thompson, F.L.; Gevers, D.; Thompson, C.C.; Dawyndt, P.; Naser, S.; Hoste, B.; Munn, C.B.; Swings, J. Phylogeny and molecular identification of vibrios on the basis of multilocus sequence analysis. Appl. Environ. Microbiol. 2005, 71, 5107–5115. [Google Scholar] [CrossRef] [Green Version]
  43. Valdes, A.M.; Walter, J.; Segal, E.; Spector, T.D. Role of the gut microbiota in nutrition and health. BMJ 2018, 361, k2179. [Google Scholar] [CrossRef] [Green Version]
  44. Ofek, T.; Lalzar, M.; Izhaki, I.; Halpern, M. Intestine and spleen microbiota composition in healthy and diseased tilapia. Anim. Microbiome 2022, 4, 50. [Google Scholar] [CrossRef]
  45. Llewellyn, M.S.; McGinnity, P.; Dionne, M.; Letourneau, J.; Thonier, F.; Carvalho, G.R.; Creer, S.; Derome, N. The biogeography of the atlantic salmon (Salmo salar) gut microbiome. ISME J. 2016, 10, 1280–1284. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  46. Eilers, H.; Pernthaler, J.; Amann, R. Succession of Pelagic Marine Bacteria during Enrichment: A Close Look at Cultivation-Induced Shifts. Appl. Environ. Microbiol. 2000, 66, 4634–4640. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  47. Thompson, F.L.; Iida, T.; Swings, J. Biodiversity of Vibrios. Microbiol. Mol. Biol. Rev. 2004, 68, 403–431. [Google Scholar] [CrossRef] [Green Version]
  48. Austin, B.; Austin, D.A. Aeromonadaceae representative (Aeromonas salmonicida). In Bacterial Fish Pathogens, Disease of Farmed and Wild Fish; Springer: Cham, Switzerland, 2016. [Google Scholar] [CrossRef]
  49. Mann, B.C.; Bezuidenhout, J.J.; Swanevelder, Z.H.; Grobler, A.F. MinION 16S datasets of a commercially available microbial community enables the evaluation of DNA extractions and data analyses. Data Brief 2021, 36, 107036. [Google Scholar] [CrossRef]
  50. Rozas, M.; Brillet, F.; Callewaert, C.; Paetzold, B. MinION Nanopore Sequencing of Skin Microbiome 16S and 16S-23S rRNA Gene Amplicons. Front. Cell Infect. Microbiol. 2021, 11, 806476. [Google Scholar] [CrossRef] [PubMed]
  51. Huang, Q.; Sham, R.C.; Deng, Y.; Mao, Y.; Wang, C.; Zhang, T.; Leung, K.M.Y. Diversity of gut microbiomes in marine fishes is shaped by host-related factors. Mol. Ecol. 2020, 29, 5019–5034. [Google Scholar] [CrossRef] [PubMed]
  52. Roques, S.; Deborde, C.; Richard, N.; Skiba-Cassy, S.; Moing, A.; Fauconneau, B. Metabolomics and fish nutrition: A review in the context of sustainable feed development. Rev. Aquac. 2018, 12, 261–282. [Google Scholar] [CrossRef] [Green Version]
  53. Díaz, E.; Ferrández, A.; Prieto, M.A.; García, J.L. Biodegradation of aromatic compounds by Escherichia coli. Microbiol. Mol. Biol. Rev. 2001, 65, 523–569, table of contents. [Google Scholar] [CrossRef] [Green Version]
  54. Rimoldi, S.; Torrecillas, S.; Montero, D.; Gini, E.; Makol, A.; Valdenegro, V.V.; Izquierdo, M.; Terova, G. Assessment of dietary supplementation with galactomannan oligosaccharides and phytogenics on gut microbiota of European sea bass (Dicentrarchus Labrax) fed low fishmeal and fish oil based diet. PLoS ONE 2020, 15, e0231494. [Google Scholar] [CrossRef]
  55. Dalsgaard, J.; Lund, I.; Thorarinsdottir, R.; Drengstig, A.; Arvonen, K.; Pedersen, P.B. Farming different species in RAS in Nordic countries: Current status and future perspectives. Aquac. Eng. 2013, 53, 2–13. [Google Scholar] [CrossRef]
Figure 1. Diversity index of Atlantic Salmon intestinal microbiota between salinity treatments. FW: Fresh water previous treatment group, GSC: gradual salinity change at 10 PSU, 20 PSU, and 32 PSU groups; 32PSU-SS Salinity shock at 32-PSU group; 32PSU-FD: Salinity shock at 32 PSU group previously feeding with a functional diet. (A) PCoA plot of the beta diversity of microbiomes calculated by Bray-Curtis dissimilarity; (B) The Simpson’s 1-D; (C) Shannon diversity index; and (D) Pielou’s evenness.
Figure 1. Diversity index of Atlantic Salmon intestinal microbiota between salinity treatments. FW: Fresh water previous treatment group, GSC: gradual salinity change at 10 PSU, 20 PSU, and 32 PSU groups; 32PSU-SS Salinity shock at 32-PSU group; 32PSU-FD: Salinity shock at 32 PSU group previously feeding with a functional diet. (A) PCoA plot of the beta diversity of microbiomes calculated by Bray-Curtis dissimilarity; (B) The Simpson’s 1-D; (C) Shannon diversity index; and (D) Pielou’s evenness.
Microorganisms 11 00076 g001
Figure 2. Relative abundance of intestinal Atlantic Salmon microbiota composition. FW: Fresh water previous treatment group; GSC: gradual salinity change at 10 PSU, 20 PSU, and 32 PSU groups; 32PSU-SS Salinity shock at 32-PSU group; 32PSU-FD: Salinity shock at 32 PSU group previously feeding with a functional diet. (A) microbiota abundance at the phylum level; (B) Top 25 most abundant taxa at genus level between treatments.
Figure 2. Relative abundance of intestinal Atlantic Salmon microbiota composition. FW: Fresh water previous treatment group; GSC: gradual salinity change at 10 PSU, 20 PSU, and 32 PSU groups; 32PSU-SS Salinity shock at 32-PSU group; 32PSU-FD: Salinity shock at 32 PSU group previously feeding with a functional diet. (A) microbiota abundance at the phylum level; (B) Top 25 most abundant taxa at genus level between treatments.
Microorganisms 11 00076 g002
Figure 3. Heat map of normalized relative abundances of the Atlantic salmon intestine core microbiota among all experimental groups. FW: Fresh water previous treatment group; GSC: gradual salinity change at 10 PSU, 20 PSU, and 32 PSU groups; 32 PSU-SS Salinity shock at 32-PSU group; 32 PSU-FD: Salinity shock at 32 PSU group previously feeding with a functional diet. (A) Core microbiota at the order level; (B) Core microbiota composition at the genus level.
Figure 3. Heat map of normalized relative abundances of the Atlantic salmon intestine core microbiota among all experimental groups. FW: Fresh water previous treatment group; GSC: gradual salinity change at 10 PSU, 20 PSU, and 32 PSU groups; 32 PSU-SS Salinity shock at 32-PSU group; 32 PSU-FD: Salinity shock at 32 PSU group previously feeding with a functional diet. (A) Core microbiota at the order level; (B) Core microbiota composition at the genus level.
Microorganisms 11 00076 g003
Figure 4. Relative abundance of intestinal Atlantic Salmon microbiota composition at the genus level in seawater groups. 32PSU-GSC: gradual salinity change at 32 PSU group; 32 PSU-SS Salinity shock at 32-PSU group; 32 PSU-FD: Salinity shock at 32 PSU group previously feeding with a functional diet.
Figure 4. Relative abundance of intestinal Atlantic Salmon microbiota composition at the genus level in seawater groups. 32PSU-GSC: gradual salinity change at 32 PSU group; 32 PSU-SS Salinity shock at 32-PSU group; 32 PSU-FD: Salinity shock at 32 PSU group previously feeding with a functional diet.
Microorganisms 11 00076 g004
Figure 5. Relative abundance proportion of metabolic pathway (level 2). FW: Fresh water previous treatment group, GSC: gradual salinity change at 10 PSU, 20 PSU, and 32 PSU groups; 32 PSU-SS Salinity shock at 32-PSU group; 32 PSU-FD: Salinity shock at 32 PSU group previously feeding with a functional diet. (A) Metabolic pathways abundance in freshwater (FW) and different seawater treatment; (BD) STAMP analysis of level 2 metabolic pathways with different abundance among samples at 32 PSU. PICRUSt2 inferred metabolic pathways with a filter size of 0.5.
Figure 5. Relative abundance proportion of metabolic pathway (level 2). FW: Fresh water previous treatment group, GSC: gradual salinity change at 10 PSU, 20 PSU, and 32 PSU groups; 32 PSU-SS Salinity shock at 32-PSU group; 32 PSU-FD: Salinity shock at 32 PSU group previously feeding with a functional diet. (A) Metabolic pathways abundance in freshwater (FW) and different seawater treatment; (BD) STAMP analysis of level 2 metabolic pathways with different abundance among samples at 32 PSU. PICRUSt2 inferred metabolic pathways with a filter size of 0.5.
Microorganisms 11 00076 g005
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Morales-Rivera, M.F.; Valenzuela-Miranda, D.; Nuñez-Acuña, G.; Benavente, B.P.; Gallardo-Escárate, C.; Valenzuela-Muñoz, V. Atlantic Salmon (Salmo salar) Transfer to Seawater by Gradual Salinity Changes Exhibited an Increase in The Intestinal Microbial Abundance and Richness. Microorganisms 2023, 11, 76. https://doi.org/10.3390/microorganisms11010076

AMA Style

Morales-Rivera MF, Valenzuela-Miranda D, Nuñez-Acuña G, Benavente BP, Gallardo-Escárate C, Valenzuela-Muñoz V. Atlantic Salmon (Salmo salar) Transfer to Seawater by Gradual Salinity Changes Exhibited an Increase in The Intestinal Microbial Abundance and Richness. Microorganisms. 2023; 11(1):76. https://doi.org/10.3390/microorganisms11010076

Chicago/Turabian Style

Morales-Rivera, María F., Diego Valenzuela-Miranda, Gustavo Nuñez-Acuña, Bárbara P. Benavente, Cristian Gallardo-Escárate, and Valentina Valenzuela-Muñoz. 2023. "Atlantic Salmon (Salmo salar) Transfer to Seawater by Gradual Salinity Changes Exhibited an Increase in The Intestinal Microbial Abundance and Richness" Microorganisms 11, no. 1: 76. https://doi.org/10.3390/microorganisms11010076

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop