Open access peer-reviewed chapter

An Insightful Model to Study Innate Immunity and Stress Response in Deep‐Sea Vent Animals: Profiling the Mussel Bathymodiolus azoricus

Written By

Raul Bettencourt, Inês Barros, Eva Martins, Inês Martins, Teresa Cerqueira, Ana Colaço, Valentina Costa, Domitília Rosa, Hugo Froufe, Conceição Egas, Sergio Stefanni, Paul Dando and Ricardo S. Santos

Submitted: 10 November 2016 Reviewed: 21 February 2017 Published: 16 August 2017

DOI: 10.5772/68034

From the Edited Volume

Organismal and Molecular Malacology

Edited by Sajal Ray

Chapter metrics overview

1,779 Chapter Downloads

View Full Metrics

Abstract

Deep‐sea environments are, in some cases, largely unexplored ecosystems, where life thrives driven by the geochemical features of each location. Among these environments, chemosynthesis‐based ecosystems, in the Mid Atlantic Ridge, have an exclusive combination of high depth, high sulfur, and high methane concentrations. This is believed to modulate the biological composition of vent communities and influence the overall vent animal transcriptional activity of genes involved in adaptation processes to extreme environments. This opens, thus, the possibility of finding gene expression signatures specific to a given hydrothermal vent field. Regardless of the extreme physicochemical conditions that characterize deep‐sea hydrothermal vents, the animals dwelling around the vent sites exhibit high productivity and thus must cope with toxic nature of vent surrounding, seemingly deleterious to the animals, while developing surprisingly successful strategies to withstand adverse environmental conditions, including environmental microbes and mechanical stress whether ensuing from animal predation or venting activity. The deep‐sea vent mussel Bathymodiolus azoricus has adapted well to deep‐sea extreme environments and represents the dominating faunal community from hydrothermal vent sites in the Mid‐Atlantic Ridge, owing its successful adaptation and high biomasses to specialized exploitation of methane and sulfide sources from venting activity. Its extraordinary capabilities of adapting and thriving in chemosynthesis‐based environments, largely devoid of photosynthetic primary production and characterized by rapid geochemical regime changes are due to symbiotic associations with chemosynthetic bacteria within its large gills. In an attempt to understand physiological reactions in animals normally set to endure extreme deep‐sea environments, our laboratory has undertaken, for the last few years, a series of investigations, aimed at characterizing molecular indicators of adaptation processes of which components of the host defense system has received most attention. This study reviews recent advances on the characterization of molecules and genes participating in immune reactions, using in vivo and ex vivo models, to elucidate cellular and humoral defense mechanisms in vent mussels and the strategies they have adopted to survive under extreme environments.

Keywords

  • innate immunity
  • deep‐sea hydrothermal vents
  • chemosynthetic ecosystems
  • long‐term acclimatization
  • host‐symbionts interactions
  • endosymbionts
  • differential gene expression
  • transcriptomics
  • mollusc bivalve
  • hydrothermal vent mussel
  • Bathymodiolus azoricus

1. Introduction

Deep‐sea hydrothermal vents were discovered 40 years ago in the Galapagos Rift [1] revealing for the first time, to the amazement of the scientific community, unusual life forms that have developed unique biochemical adaptations to high temperatures and toxic chemical nature of vent surrounding, otherwise harmful to life as we know it on the surface of the planet [25]. The animals dwelling around the vent sites exhibit high productivity and thus must cope with the seemingly deleterious physical and chemical conditions, while developing surprisingly successful strategies to withstand adverse environmental conditions, including environmental microbes and mechanical stress whether due to animal predation or from deep‐sea volcanic eruptions [68].

At such depths and in the absence of light, life is thriving in chemosynthesis‐based ecosystems where most abundant marine invertebrates have developed mutualistic relationships with chemosynthetic bacteria. These symbiotic interactions are believed to play a crucial role in the survival of hydrothermal vent animals, driving their transcriptional activities, and their successful adaptation strategies to subsist under extreme environmental conditions. They essentially rely on the establishment of endosymbiosis relationships between vent animals and sulfur‐oxidizing (SOX) or methane‐oxidizing (MOX) bacteria [913].

Deep‐sea vent mussels of the Bathymodiolus genus are dominant members at hydrothermal vents and cold seep habitats. These mussels have the peculiarity of sheltering both endosymbiotic sulfide‐oxidizing and methane‐oxidizing bacteria in their gills [913], supporting thus their endurance within this type of environment. Bathymodiolus azoricus is also the dominant species in deep‐sea hydrothermal vents in the Azores region and is well adapted to extreme conditions particularly to toxic concentrations of heavy metals, acidic pH, and absence of light [1417].

In an attempt to understand physiological reactions of animals normally set to endure extreme conditions, in deep‐sea environments, our laboratory has undertaken, for the last 6 years, a series of investigations aimed at characterizing molecular indicators of adaptation processes of which components of the immune and stress‐related systems have received most of our attention [18, 19]. Central to our studies is the long‐term maintenance of vent mussels to atmospheric pressure proven to be a useful model to study unique molecular relationships under which the regulation of gene transcription may be affected by aquaria conditions and by the gradual disappearance of endosymbiont bacteria from gill epithelia [20]. Nonetheless, vent mussels subsist for months at atmospheric pressure in aquaria supplemented with plain sea water in or with artificial diet. This has allowed us to focus on developing experiments to investigate new physiological responses of animals sustaining experimental challenges involving immunological and stress‐related reactions and to provide new approaches to assess the effect of natural microorganisms and metal toxicity at vent environments [21, 22]. As a research model, the choice of the vent mussel B. azoricus is of great significance given its unique symbiosis with SOX and MOX bacteria. It has provided us with the means to understanding the molecular mechanisms underlying immune reactions in animals normally set to endure extreme deep‐sea environments and the role of their symbiotic bacteria in controlling immune gene transcriptional activity.

In line with this, we have investigated main constituents of the vent mussel immune system and demonstrated how immune and stress genes could be modulated upon different experimental challenges in the absence of the characteristic high hydrostatic pressure found at deep‐sea vent sites without methane and/or sulfide supplementation [2123]. The proximity to the nearby hydrothermal vent fields, in the Azores region, has given us a geographical advantage for earning first insight into immediate physiological responses comprising both cellular and humoral responses of live mussels, freshly collected from the hydrothermal vents, which upon arrival, are acclimatized to our aquarium system, LabHorta [2325]. The maintenance of live mussels in our laboratory is thus a key factor in gaining knowledge into the physiology of vent animals including the study of evolutionary conserved immune, inflammatory, and stress‐related factors commonly found in other marine bivalves [19, 26].

Advertisement

2. Innate immunity in Bathymodiolus azoricus

The interaction between microorganisms and host defense mechanisms is a decisive factor for the survival of marine bivalves. They rely on cell‐mediated and humoral reactions to overcome the pathogens that naturally occur in the marine environment [27]. Growing interest in deep‐sea vent biology has turned the vent mussel B. azoricus into a model organism centered on research activities based on the premise that vent mussels clearly have need for an immune system to overcome microbial challenges in their natural surroundings. For this reason, our research strategies have been focused on the molecular characterization of molecules participating in immune reactions, using in vivo and ex vitro models, to elucidate cellular and humoral defense mechanisms in vent mussels and its survival strategies under extreme environments. As for other bivalves, the innate immune system of B. azoricus is based on cellular constituents and soluble hemolymph (blood) factors, which play a prominent role in protecting the animals against invading microorganisms. The circulating hemocytes or blood cells are mostly found in the hemolymph and extrapallial fluid. They are responsible for cell‐mediated defense reactions such as phagocytosis and the activation of a variety of cytotoxic reactions including the release of lysozomal enzymes and antimicrobial peptides [2830]. Moreover, the generation of highly reactive oxygen intermediates (ROIs) and nitric oxide also plays an important defense role against pathogens [3033]. Besides their decisive role in protecting the host from microbial assaults, bivalve hemocytes have also been implicated in other important physiological functions, including nutrient transport, digestion, wound healing and shell regeneration and/or mineralization, and excretion [34]. In addition, the hemolymph serum contains humoral defense factors such as lectins and cytokine‐like molecules that are directly and indirectly involved in the killing of pathogens and in mediating cell‐cell interactions, respectively. Lectins are important mediators of cellular reactions and exhibit opsonin properties, which facilitate the phagocytosis [3539]. The hemolymph also contains antibacterial factors and lysozomal components that ensure, along with hemocyte phagocytic and cytotoxic processes, the clearance of pathogenic bacteria [38, 39]. Using a combination of light microscopy and staining procedures, three major hemocyte types are discernible in the extrapallial fluid and hemolymph of B. azoricus. The most abundant type was identified as granulocyte readily recognizable by their cytoplasmic granules [19]. They appear fairly homogeneous in size and showing a characteristic crescent, or half‐moon shape morphology upon adherence to glass slides and before migratory movements. Granulocytes spread well onto the glass surface averaging 30–40 μm in length. In contrast, hyalinocytes presented smoother cytoplasm, i.e., a nongranular appearance due to a lower amount of cytoplasmic granules noticeable under phase contrast and differential interference contrast visualizations [19]. A third less common hemocyte type was also observed. They correspond to hemoblast‐like cells and presented a spherical shape appearance with higher nucleus to cytoplasm ratio when compared to granulocytes and hyalinocytes [19]. In vitro phagocytic assays carried out with B. azoricus hemocytes revealed that 70% of the hemocytes containing more than two zymosan particles were granulocytes and to a lesser extent the percentage of phagocytic cells corresponding to hyalinocytes was 23%. In contrast, the percentage of hemoblasts containing ingested zymosan particles was 5–7%, the lowest revealed in our studies [19].

Along with hemocytes studies, we began to tackle signaling pathways putatively involved in the mediation of cellular responses in the presence of Vibrio spp. It was demonstrated that compounds of microbial origin could trigger detectable phosphorylation events in B. azoricus hemocyte extracts and likely involving the activation of different classes of mitogen‐activated protein kinases (MAPKs). When challenged with a marine bacterium, Vibrio parahaemolyticus or a nonmarine bacterium, Bacillus subtilis, to stimulate hemocytes, cellular proteins were differently phosphorylated as demonstrated in Western blotting experiments using the MAPK/ERK, p38, and JNK rabbit polyclonal antibodies. Moreover, the differences seen in phosphorylation patterns could be attributed to inherent properties of the bacterial strain used, differences in the mechanisms of binding to hemocytes, or differential activation of cell membrane receptors and signaling pathways, resulting in different patterns of protein phosphorylation. Western blotting analyses suggest that B. azoricus hemocytes display receptors with binding affinities toward microbial molecules or to live bacteria [19].

Advertisement

3. Ex vivo experiments with gill tissues: new insights into tissue immune specificity toward microorganisms

As mytilid species, the deep‐sea vent mussel B. azoricus exhibits large lamellated gills (ctenidia) arranged as numerous filament structures stacked together through ciliary junctions. Each filament is organized in two coalescent epithelial cell sheets overlaying a central lumen where hemocytes can be found. The thinness of gill filaments allows for the visualization of live hemocytes through the epithelium, and to monitor hemocyte motility directly under light microscopy [19]. Bivalve mollusk gills assume thus a strategic importance at the interface between the external milieu and the internal body cavities of the animal where contact with microorganisms is inevitable during feeding processes inasmuch as host defense responses may incur from interactions with infective pathogens during normal filtration [3639]. For this reason, a number of typical cellular and humoral immune reactions are likely to take place in gill tissues and observable as hemocyte proliferation and phagocytosis, the activation of immune signaling pathways, and the activation of genes involved in immune, antioxidant and antibacterial responses against invading bacterial pathogens or the presence of metal toxicants [3639].

To further test the gill’s ability to mount immune reactions, a series of ex vivo experiments have been performed using gill tissues freshly dissected from vent mussels and subjected to short‐term incubations in tissue culture well‐plates and under different experimental settings. Different stimuli were carried out to demonstrate the expression of genes in gill tissues exposed to a mixture of endosymbionts previously obtained from gill extracts, and V. parahaemolyticus, in comparison with sterile sea water incubations (Figure 1). Differential gene expression results indicated that exposure to methanotrophic and thiotrophic endosymbiont preparations led to general upregulation of genes involved in immune recognition reactions, without the addition of hemolymph, while gill incubations with endosymbiont extract and to which hemolymph serum (hemocyte free) was added led to an opposite effect, resulting in a lower expression of immune recognition genes. These results contrasted with incubations performed with V. parahaemolyticus or with control sterile sea water. In this case, higher levels of gene expression were achieved when hemolymph was added to gill tissues incubated with V. parahaemolyticus or control sterile sea water (Figure 1). Ex vivo experiments as described bring evidence supporting a yet uncharacterized effect of hemolymph and its humoral constituents over endosymbionts, likely controlling immune gene expression of its host B. azoricus. This prompted the question of whether the host gill tissue would be able or not to recognize endosymbiont as self‐particles and to which extent the host immune system does not disturb the acquisition of endosymbionts by horizontal transfer during the host larval stages. Moreover, the permanence and survival of endosymbionts within gill tissue would require a fitted control over the host immune system, acting on the transcriptional regulation of immune genes and at the level of pattern recognition receptors (PRRs) expressed by cells of the host innate immune system to detect microbial‐associated molecular patterns (MAMPs) present on the surface of microorganisms [40, 41]. This endosymbiont effect over the host immune system would likely require the presence of hemolymph and its humoral constituents, as demonstrated by the gill ex vivo experiments (Figures 1 and 2). Since the gill tissue does grow over the mussel life’s time we also probed different gill sections to determine levels of immune gene expression along the anterior‐posterior axis, notably the “budding zone” on the posterior end, considered as the youngest section of the gill and through which endosymbionts are believed to make their entry. It was found that vent mussel gene expressions were markedly lower than other gill tissue sections, suggesting a thigh mechanism of transcriptional regulation of host genes in the presence of endosymbiont bacteria in the gill budding zone.

Figure 1.

Ex vivo experiments performed with dissected gills. Gill fragments were incubated with V. parahaemolyticus and with an enriched preparation of endosymbionts freshly obtained from gill homogenates and gradient centrifugation. The effect of hemolymph humoral factors was tested by incubating gill fragments with and without hemolymph in the presence of V. parahaemolyticus and endosymbiont mixture. Results were compared to control incubations with plain sterile sea water. Gene expression was performed by qPCR targeting the immune recognition genes Aggrecan, C‐type lectin, C‐type lectin immune receptor, immune lectin receptor, lipopolysaccharide‐binding protein‐bactericidal/permeability‐increasing protein, peptidoglycan recognition protein, and serine protease inhibitor‐2 [50]. Incubations performed with endosymbiont preparations distinctively induced immune recognition genes in the absence of hemocyte‐free hemolymph.

Figure 2.

Ex vivo experiments performed with dissected gills. As in Figure 1, gill fragments were incubated with distinct bacterial stimulants: an enriched methanotrophic bacterial preparation; an enriched thiotrophic bacterial preparation, a mixture of methanotrophic and thiotrophic bacterial preparations, Vibrio parahaemolyticus and Photobacteria bacterium. Results were compared to control incubations with plain sterile sea water. Gene expression was performed by qPCR targeting same immune recognition genes as in Figure 1. Separate methanotrophs and thiotrophs preparations induced higher levels of immune gene expressions when compared to a mixture of the two endosymbiont bacteria preparations. Incubations using Vibrio parahaemolyticus resulted in drastic downregulation of immune recognition genes.

As filter feeders living most of their lives attached to a substrate, bivalves are exposed to constant biologically available pollutants over an extended period of time [4244]. They have been studied as biological models to assess the impact of pollution in the environment and used as a biomonitoring “tool” due to their capacity of bioaccumulating high concentrations of trace metals, mostly in soft tissues such as gills and digestive gland [4547]. The large surface of the gills and their involvement in gas exchange and feeding processes bring bivalves to constant and intimate contact with their environment where pathogens may also find their route of entry and encounter the bivalve first‐line immune defense reactions.

While marine bivalves living in sandy, rocky intertidal, and shallow subtidal environments may rely on well‐established humoral and cellular immune reactions to counteract pathogenic microorganisms, a new level of molecular intricacy may be seen between endosymbiont‐bearing bivalves living in anaerobic and sulfide‐rich environments and the pathogenic microorganisms they encounter. These natural molecular interactions would account for the role of endosymbionts in modulating the host immunity by controlling the transcriptional activity of immune genes. Bivalve associations with chemoautotrophic endosymbionts are now well known and widely distributed across a range of different chemosynthetic environments, including deep‐sea hydrothermal vents (Bathymodiolus spp., Calyptogena sp.); gas seeps, mud volcanoes, and petroleum seeps (Bathymodiolus spp., Calyptogena sp.); whale and wood falls (Idas spp., Adipicola spp., Vesicomya sp., Axinodon sp.); and shallow water anoxic sediments mediated by sulfate reduction (Solemya spp., Codaki spp., Anodontia spp., Lucina spp.) [7].

Our recent results from ex vivo gill tissue experiment proven to be a valuable system for the study of tissue‐specific immune responses where the thin epithelial cell layers of gill filaments would make it possible to signal pathogen‐sensing directly through gill epithelia and affecting adjacent methanotrophic or thiotrophic endosymbionts which in turn would functionally prime host immune cells, the hemocytes, into altering their transcriptional activity (Figure 3). The endosymbiont immunomodulatory effect on the host immune system, as discussed in detail further below, is still under current investigations by our research team as the complexity of host‐endosymbiont interactions in the deep‐sea vent mussel B. azoricus remains to be fully understood. This model is consistent with the hypothesis that innate immune receptors are required to promote long‐term colonization by microbiota. This emerging perspective challenges current paradigms in immunology and suggests that PRRs may have evolved, in part, to mediate the bidirectional cross‐talk between microbial symbionts and their hosts [48, 49].

Figure 3.

Hypothetical model representing the host‐endosymbiont‐mediated immune responses against pathogens. In a normal immunological state, hemocytes PRRs are being sensitized by host‐endosymbiont interactions allowing the vent mussel immune system to remain active and tolerant to the presence of MOX and SOX bacteria. Upon interacting with extracellular pathogens, host‐symbiont interactions are altered and incur in higher endosymbiont genes transcriptional activity [74] and subsequently affecting host hemocytes by triggering its immune repertoire via PRRs activation.

Advertisement

4. Posttranscriptomics studies in Bathymodiolus azoricus

In 2010 a high‐throughput sequencing and analysis of the gill tissue transcriptome from the deep‐sea hydrothermal vent mussel B. azoricus was reported by our group [50]. It represented the first tissue transcriptional analysis of a deep‐sea hydrothermal vent animal, using next generation sequencing technology, enabling the creation of a searchable catalog of genes that provided a direct method of identifying and retrieving vast numbers of novel coding sequences which could then be applied in gene expression profiling experiments, using quantitative polymerase chain reaction (qPCR), from a nonconventional model organism [50]. It provided the most comprehensive sequence resource for identifying novel genes currently available for a deep‐sea vent organism, in particular, genes putatively involved in immune and inflammatory reactions in vent mussels. This first transcriptional analysis of gill tissues from the deep‐sea hydrothermal vent B. azoricus was organized as a searchable catalog of genes providing a direct method of identifying and retrieving vast numbers of novel coding sequences, which can be applied in gene expression profiling experiments. The assembled and annotated sequences were organized in a dedicated database, accessible through the website http://transcriptomics.biocant.pt/deepSeaVent [50].

With an unprecedented high number of gene sequences available from our transcriptomic data, we were able to tackle signaling pathways and compare gene expression profiles in a series of experiments aiming at better understanding innate immunity in animals physiologically programmed to endure deep‐sea vent conditions. Responses to bacterial infections with different strains of Vibrio wound experiments, long‐term acclimatization in aquarium conditions and pressurization experiments with the hyperbaric chamber IPOCAMP [51] became the main focus of our research, setting thus the grounds for more in‐depth analyzes revealing distinct gene expression profiles behind unique molecular relationships under which the regulation of gene transcription may be affected by biotic factors including microorganisms, the presence of endosymbiont bacteria and shell damage incurring in opportunistic infections or by abiotic factor as the hydrostatic pressure. The majority of the genes comprising four functional categories as described by Bettencourt et al. [50] and relating to immune recognition, signaling transduction, transcription, and effector molecules mechanisms were analyzed by qPCR.

The long‐term aquarium maintenance of vent mussels to atmospheric pressure has long been central to our studies and proven to be a useful model to study unique molecular relationships under which the regulation of gene transcription may be affected by the gradual disappearance of endosymbiont bacteria from gill epithelia [20, 52]. Nonetheless, vent mussels from Menez Gwen hydrothermal vent site subsist for months at atmospheric pressure in aquarium conditions, in plain sea water or supplemented with methane and sulfide. This has allowed us to focus on developing experiments to investigate new physiological responses of vent mussels sustaining experimental challenges involving bacterial pathogens of the Vibrio genus, even in the absence of the characteristic high hydrostatic pressure found at deep‐sea vent sites and without methane and sulfide supplementation [21, 22].

Earlier results from experimental exposures to Vibrio splendidus, Vibrio alginolyticus, Vibro anguillarum, and Flavobacterium sp. pointed at the immune discriminatory capacity of B. azoricus to distinguish different Vibrio strains, and at significant differences of immune gene expression levels between 12 and 24 h exposure times. These studies concluded that the immune gene transcriptional activity was modulated at two levels, i.e., over the course of time and according to the bacterial strain tested, suggesting thus, a selective response toward Vibrio spp. when vent mussels were experimentally challenged during 24 h [53, 54]. Additional experiments were carried out with Vibrio diabolicus aiming at the analysis of gene expression differences between distinct vent mussel populations from the hydrothermal vent sites Menez Gwen (MG, 800 m depth) and Lucky Strike (LS, 1700 m depth) both located on the Mid‐Atlantic region, near the Azores islands. These comparative studies revealed unique immune transcriptional specificities at the gill, digestive gland, and mantle tissues level providing further evidence supporting different usage of transcription factors at the promoter region of immune genes possibly linked to the hydrothermal vent environment Furthermore, Menez Gwen (MG) and Lucky Strike (LS) B. azoricus showed significant gene expression differences during V. diabolicus challenges over time demonstrating that immune genes are differentially expressed within the same mussel populations regardless of their hydrothermal vent origin suggesting thus site‐related tissue‐specific gene expression patterns [55]. Moreover, these results also suggested different tissue tolerance to decompression and adaptation to atmospheric pressure not seen so far. Mantle tissues from LS mussels seemed unaffected by deep‐sea retrieval showing significantly higher levels of immune gene expressions as compared to MG mantle tissues. Thus, the decompression effect on the animal’s internal organs may be evaluated by ways of its ability to respond, at the immune transcriptional level, to V. diabolicus challenges. For that reason, mantle tissues from LS animals appear to be decompression‐resistant and immune competent toward bacterial challenges. On the other hand, the digestive gland revealed the most increased gene expression levels in MG animals showing how the tissue microenvironment is relevant to in situ immune responses. Gill immune transcriptional activity in both MG and LS mussels was not as significantly different as for the other tissues tested which may be attributed to the presence of endosymbiont bacteria in gill epithelia acting as a driving factor likely to affect host‐gene expression and the overall physiological statuses of MG and LS vent mussels while interacting with V. diabolicus. Even though gill tissues have been the main focus of most of our previous investigations in the deep‐sea vent mussel B. azoricus, the digestive gland and mantle tissues hold the potential for highlighting specific immune responses in tissues other than gills and how they can modulate the outcome of the animal’s overall immune responses [55].

In addition to ex vivo experiments and Vibrio exposures to live vent mussels, we were able to carry out long‐term acclimatization experiments with vent mussels kept in aquaria and at atmospheric pressure. These experiments were devised to assess the effect of such prolonged aquarium conditions on immune and stress‐related reactions as mussels were gradually releasing their endosymbiont bacteria from gill bacteriocytes. These studies provided a basis for understanding the interactions between host‐immune and endosymbiont gene expressions during postcapture long‐term acclimatization in plain sea water and represented an ideal model for investigating B. azoricus immune genes transcriptional activity and symbiont bacteria prevalence, in view of changes in the availability of chemical‐based energy sources during acclimatization at atmospheric pressure. It also pointed out the relevance of gene expression studies while addressing the swift changes affecting metabolic adaptations and food intake fluctuations, whether induced by or as a result of the gradual loss of endosymbionts and subsequent presence of symbiont bacteria in the aquarium environment, altering thus the physiological homeostasis of B. azoricus [56]. These studies demonstrated that the transcriptional activity profiles for immune and bacterial endosymbiont genes followed a time‐dependent mRNA transcriptional pattern evidenced at 24 h, 1 week, and 3 weeks acclimatization. Furthermore, after 1 week acclimatization, vent mussels were under the influence of what appears to be a concomitant host‐immune and endosymbiont gene expression, possibly indicating a physiological transition point which induces higher levels of transcriptional activity [56]. Under such circumstances, survival of vent mussels will require immune gene repertoire switching involving the differential expression (DE) of recognition, signaling, transcription, and effector genes tied to environmental parameters and to the symbiotic relationships in B. azoricus. Metabolic adaptations and food intake changes, whether induced as a result of the gradual loss of endosymbionts and subsequent release in the aquarium environment, are likely to affect gene transcription activities and prevalence of symbionts in gill tissues [5658].

The geographic proximity to the nearby hydrothermal vent fields, in the Azores region, gave our laboratory a positional advantage for earning first insight into immediate physiological responses comprising both cellular and humoral responses of freshly collected mussels from different hydrothermal vents, which upon arrival, are acclimatized to our aquarium system, LabHorta [23].The maintenance of live mussels from the shallower vent field, Menez Gwen, became thus a key factor in gaining knowledge into the physiology of vent animals including the study of evolutionary conserved immune, inflammatory and stress‐related factors commonly found in other marine bivalves [1822].

Taking advantage of the LabHorta facility, comparisons studies were made possible, with live vent mussels subjected to V. parahaemolyticus infection, wound injury, hyperbaric pressurization, and 3 months acclimatization (Figure 4). These experiments allowed for the characterization of the differential activation of signaling pathways and the relative quantification of immune genes expressed during each type of stimulation. Differential gene expression results indicated that the four experimental conditions tested were distinctively inducing the immune genes of vent mussels to different levels of transcriptional activity of which the immune and signal transduction genes showed the highest expressions (Figure 5).

Figure 4.

Schematic representation of immune signaling activation. After initial events characterized by immune recognition and stress‐related reactions, signal transduction pathways are induced into transmitting a series of protein phosphorylation events, through the intracellular milieu, which ultimately result in the translocation of transcription factors into the nucleus that initiates the transcription of genes encoding immune effector molecules, here represented as lysozyme, metallothionein, and ferritin.

Figure 5.

Comparative gene expression profiles from vent mussels subjected to 3 months acclimatization in aquaria at atmospheric pressure; Vibrio parahaemolyticus exposures; wound injury, and repressurization in the IPOCAMP chamber. Results are presented as relative expression folds calculated by qPCR and targeting immune genes from recognition, signaling transduction, transcription and effector functional gene categories as defined in Bettencourt et al. [50].

Of the four challenging conditions V. parahaemolyticus infections resulted in the highest number of genes with higher level of expression during this comparison study based on qPCR and selected genes targeting immune recognition, signal transduction, transcription, and synthesis of effector molecules processes (Figure 5). Also, cross‐talk between signaling pathways may occur in B. azoricus individuals subjected to Vibrio infections, wound responses, and hyperbaric stimulations, i.e., same immune or pro‐inflammatory signaling molecules may serve different signaling pathways whether they are conspicuously more expressed or not during such experiments. Cleary, the activation of signaling pathways involved in Vibrio infections was distinct from that of wound and hyperbaric reactions and thus conferring the animal model presented here with the physiological versatility to cope with deep‐sea hydrothermal vent environments. These experiments were important to elucidate the molecular mechanisms under which, physiological responses to bacterial infections, would responses, hyperbaric stimulations and long‐term maintenance in aquaria conditions, may be involved in B. azoricus adaptation processes whether in deep‐sea vent environments or at atmospheric pressure. However, in‐depth analysis of different signaling genes and pathways involved in such experimental challenges remained fragmentary and elusive.

One the most common goals of RNA Sequencing (RNA‐Seq) profiling is to identify genes or molecular pathways that are differentially expressed (DE) between two or more biological conditions [5963]. Changes in expression can then be associated with differences in physiological reactions, providing clues for further investigation into potential mechanisms of action [64, 65]. In order to gain additional insight into the different signaling genes involved in Vibrio infection, wound response, long‐term acclimatization, and hyperbaric repressurization, we sequenced the full transcriptome of gill tissues from each of these experimental challenges to which deep‐sea vent mussels were subjected and compared their differential gene expression levels with that of gene expression in animals immediately retrieved from the vent sites with the help of acoustically trigged cages that were recovered at the sea surface. Transcript sequences for the five cDNA libraries were obtained from the Illumina RNA‐sequencing platform and de novo assembly of RNA‐Seq transcripts performed with Trinity [66, 67] followed by differential expression (DE) analyses using the edgeR package [6870]. DE results were presented as Heatmaps clusters (transcriptional cluster report for edgeR DE analysis). The advantage of Heatmaps is that it can display the expression pattern of the genes across all the RNA samples. Visualization of the results is aided by clustering together genes that have correlated expression patterns [68].

Here we present examples of expression plots for some of the most DE genes across the five different experimental conditions referred to as “cage,” animals freshly collected with acoustically triggered cages, from the bottom of the deep‐sea vent floor; “3 months,” same animals as in “cage” acclimatized for 3 months in aquaria environment at 1 atm; “Vibrio,” same animals as in 3 months exposed to V. parahaemolyticus; “Wound,” same animals as in 3 months with shell injury caused by mechanical abrasion to expose the mantle; “IPOCAMP,” same animals as in 3 months subjected to 80 bar hydrostatic pressure for 72 h. The top‐scoring BLAST hit for each of the gene exemplified is shown on top of the respective expression plot (Figure 6).

Figure 6.

Expression plots across the five experimental conditions, “3 months”; “IPOCAMP”; “cage”; “Vibrio,” and “Wound,” representing differential gene expression analyses using EdgeR. The top‐scoring BLAST hit for each of the genes exemplified is shown on top of the respective expression plot.

Comparison of DE across the five experiment revealed interesting correlations as for “cage” and “3 months” mussels indicating that vent mussels endured well aquarium conditions for as long as 3 months, as demonstrated by similar levels of gene expression. Vibrio infections and IPOCAMP pressurization also showed clustering patterns of gene expression which would seem to indicate that once mussels are acclimatized to atmospheric pressure, repressurization stimulus is impacting vent mussels in similar ways as in V. parahaemolyticus challenges, suggesting thus the occurrence of stress‐related reactions in both types of stimulations. The expression pattern seen for wound injury was particularly distinct as compared to the other four experimental conditions. Wound injury seemed to affect drastically the vent mussel transcriptional activity which some of its genes were severely downregulated probably due to the damaging effect caused by the mechanical abrasion and direct exposure of the mantle to the aquarium environment. Taken together these experiments proven to be insightful in demonstrating the contrasting behavioral expression of given important physiological transcripts such as the peptidoglycan recognition and LBP‐BPI proteins, both involved in innate immune responses, when vent mussels are met with distinct environment factors.

Advertisement

5. Host‐endosymbiont interactions: implications for host immunity and defense mechanisms against bacterial pathogens

The transcriptome sequencing of gill tissues from the mussel B. azoricus revealed a set of genes of bacterial origin, providing a functional insight into the microbial vent community [71]. The transcripts supported a metabolically active microbiome and a variety of bacterial mechanisms and pathways, among which the fixation of carbon, the use of nitrate as a terminal acceptor of electrons and oxidation of sulfur and methane. The bacterial genes ensued from this sequencing work were deemed relevant to evaluate the influence of abiotic and biotic environmental conditions on B. azoricus transcriptional activity and also potentially useful to assess symbiont density differences in vent animals originated from distinct hydrothermal vent sites, respectively, to their environmental settings [72]. Keeping in line with the assumption that geographically distinct vent mussels will adopt different physiological statuses in relation to their environmental conditions, we also surmised that the relative abundance of methanotrophic and sulfide oxidizing endosymbiotic bacteria would differ between the Menez Gwen and Lucky Strike mussels as previously reported by other researchers [12, 58, 73]. We hypothesized that geographically distinct B. azoricus individuals may be experimentally traced back to their original hydrothermal vent sites based on their bacterial transcriptional activity and bacterial gill densities at the time animals were retrieved from the shallower Menez Gwen and deeper Lucky Strike vent sites. A taxonomical structure of the vent mussel gill’s microbiome was also assessed to determine the bacterial community composition of gill tissue from MG and LS mussels to infer the symbiont densities differences between animals from both vent sites. Results from the ribosomal RNA amplicon sequencing of the V6 hypervariable regions, by massive parallel 454 pyrosequencing, indicated that the percentage of sequences obtained was from endosymbiont bacteria at nearly the same proportion between Menez Gwen and Lucky Strike samples. Moreover, comparative analyses based on BLAST searches in the RDP database, using the 16S rRNA OTU sequences, revealed that the thiotrophic endosymbiont represented 90% of all the sequences and methanotrophic endosymbiont almost 5% of the sequences from vent mussel samples originated from the distinct Menez Gwen and Lucky Strike hydrothermal vent fields [72].

While the majority of our experiments using live vent mussels were performed shortly after their retrieval from the Menez Gwen hydrothermal vent, long‐term studies with vent mussels acclimatized to atmospheric pressure conditions have hardly been addressed until recently. As above‐mentioned, long‐term acclimatization experiments in aquarium systems have allowed us to study the expression of bacterial symbionts genes, particularly methanotrophic and thiotrophic bacteria, over time of acclimatization while their mussel host is faced with drastic physiological challenges, metabolic adaptations, and food intake changes in an effort to adapt to an aquarium environment at atmospheric pressure and without supplementation of methane and sulfur [56]. The physiological adaptation to aquarium environment is likely to be aggravated by the expelling of endosymbionts into the aquarium environment, progressively emptying the gill tissue of its autotrophic bacteria, essential for the host vent mussel nutritional sustenance. Long‐term aquarium acclimatization represents thus a model study to investigate the presence and maintenance of symbiotic associations between chemosynthetic bacteria and vent animals, which depend on controlled cell‐cell communication between host and endosymbionts and the role of the host immune system [56, 74].

Presumably, the loss of endosymbiont induces a dramatic change in host gene expression profiles especially if endosymbiont genes exert some transcriptional control over host gene expression. For this reason, acclimatization studies have been instrumental to further our understanding of B. azoricus immune system. These studies have provided insights into physiological principles underlying mechanisms of adaptation to aquarium conditions at sea level pressure while taking advantage of the remarkable capacity of vent mussels to survive well decompression once brought to surface [21, 22, 56]. Furthermore, these studies have allowed analyses using immune challenged mussels comparatively to acclimatized control mussels, maintained under aquarium conditions. In view of our previous experiments performed with live gill tissues and postcapture immune gene expression studies in B. azoricus acclimatized to atmospheric pressure, the presence of endosymbiont bacteria is now being under investigation as a driving factor under which host‐immune genes may transcriptionally be modulated and reciprocally endosymbiont genes may transcriptionally be modulated by the host [5356]. Moreover, the impact of aquarium acclimatization on B. azoricus immune responses and its capacity to react to V. diabolicus challenges was recently evaluated during recurrent incubations with V. diabolicus during short periods of time, followed by clean sea water incubations allowing animals to depurate and subsequently be reexposed to the same load of V. diabolicus over a period of 3 weeks acclimatization experiment [74]. As previously described, we found a time‐dependent immune gene response in B. azoricus tied to the endosymbiont presence inside the vent mussel gills. The vent mussel’s immune defense capabilities were affected by the gradual loss of symbiont bacteria suggesting a symbiont‐mediated defense mechanism under which the transcriptional regulation of host immune genes is directly affected by symbiont density and/or activity. The host‐immune system‐endosymbiont interactions were actively higher during the first week of acclimatization as a result of Vibrio exposures, demonstrating the ability of B. azoricus to increase the transcription of immune genes while endosymbiont gene expression also correlated with an increased symbiotic metabolism and prevalence. A synergistic response was proposed to counteract the presence and potential infection by V. diabolicus bacterium while modulating B. azoricus immune defenses‐endosymbiont interactions to an extant, which host‐immune and endosymbiont genes are mutually reliant during the first weeks of acclimatization [74]. The evidence presented suggests successful V. diabolicus recognition prompting immune genes to increase their levels of transcriptional activity particularly for genes involved in the Toll‐like receptor signaling [75, 76] and apoptosis‐related pathways [77] during first day of acclimatization in aquarium environments. In agreement with this, B. azoricus is presented as a suitable model to study molecular interactions involving host‐mediated immune recognition events and adaptation mechanisms, to mitigate apoptosis harmful effects induced by Vibrio exposure against which, endosymbionts were prompted to increase their transcriptional activity, evocative of a possible protection role to the host [74]. This work brings to light other questions relating to how the host‐immune system regulates the symbiont population within their gills and conversely symbionts avoid being recognized and eliminated by the host. These topics are being further investigated in our group and focused on finding and characterizing the molecular mechanisms underlying the establishment (recognition and acquisition) and functioning of symbiosis between deep‐sea vent mussel B. azoricus and the methanotrophic and thiotrophic bacteria (gene expression, energy metabolism, regulation of symbiont population).

Interestingly, the study of intricate associations with chemosynthetic symbiont‐bacteria living in the gills of deep‐sea vent animals led us to the conception of a new pathogenesis model system based on an unconventional host‐symbiont model system. This new marine invertebrate model system, as for the ecotoxicological model Mytilus spp. [78] relies, instead, on its unique host‐immune‐symbiont bacteria interactions believed to play a crucial role in counteracting infectious pathogens. The establishment of invertebrate host pathogen systems may serve as suitable and useful models to study pathogenicity. The molecular mechanisms through which pathogens are able to colonize and overtake host’s immune system, particularly during the initial phase of infection when molecular recognition of MAMPs is occurring, as the pathogen defines its route of entry, are expected to reveal new molecular strategies that could help developing new therapies in aquaculture diseases. Using the deep‐sea vent mussel B. azoricus as an alternate invertebrate model system to study pathogenesis brings a new perspective into the search for new drug targets that could directly interfere with pathogen recognition processes and/or with in situ inflammatory process where immune cells (i.e., hemocytes) and cytokine‐like molecules are being mobilized. Indeed, in such host‐endosymbiont model systems, the role of endosymbiont‐derived molecules could have an important influence in mediating pathogenesis and in counteracting the deleterious effect of pathogens on the host immune system. From an experimental approach, several genera of bacterial fish pathogens may be used in B. azoricus, as infectious agents, e.g., Vibrio, Flavobacterium, Pseudomonas, Aeromonas, Streptococcus. Host and endosymbiont gene expression profiles may be studied during infection experiments carried with a given bacteria and genes that are markedly upregulated or downregulated further analyzed and their cDNA sequences determined by traditional sequencing methods.

Particular attention should be given to genes whose encoded proteins are participating in signal transduction pathways directly influencing the outcome of immune effector molecules, as antibacterial peptides; immune recognition lectins and antioxidant products such as superoxide dismutase, ferritin, metalloproteinases, metallothioneins, and heat shock proteins [26]. Synergistic effects resulting from interactions between host immune and endosymbiont activity, in counteracting infectious pathogens, may now be studied at the molecular level, for future therapies design, targeting key steps during pathogen infection processes, for instance, host recognition events; production of the anti‐inflammatory factor TNF‐alpha and cytokine‐like growth factors; enhancement of antibacterial molecules synthesis.

Advertisement

6. Concluding remarks

In an attempt to understand physiological reactions of animals normally set to endure extreme conditions, in deep‐sea environments, our laboratory has undertaken, for the last 6 years, a series of investigations aimed at characterizing molecular indicators of adaptation processes of which components of the immune and antioxidative stress response systems have received most of our attention. As a research goal, long‐term maintenance of vent mussels to atmospheric pressure was instrumental to further our understanding on molecular relationships under which the vent mussel‐endosymbiont interactions are affected by aquaria conditions and by the gradual disappearance of endosymbiont bacteria from gill epithelia. Hence, the maintenance of live mussels in our aquarium laboratory system has been a key factor in gaining knowledge into the physiology of vent animals including the study of evolutionary conserved immune, inflammatory, and stress‐related factors commonly found in other marine bivalves. In vivo and ex vivo experiments conducted with live mussels and their excised gill tissues as primary tissue cultures, allowed the specific host‐endosymbiont interactions to be revealed, and further characterized in the deep‐sea vent model B. azoricus, establishing distinct genetic signatures for the expression of endosymbiont genes and host‐immune genes in relation to different environmental conditions. Increasing evidence now support the role of gills as a bone fide immune‐responsive tissue in B. azoricus, consistent with a suitable study model for exploring molecular interactions involving host‐endosymbiont‐mediated immune recognition events and adaptation mechanisms to deep‐sea hydrothermal vent environments. Such adaptation mechanisms are likely to be influenced by the microbial community composition surrounding the mussel beds at hydrothermal vents and therefore it is important to continue metatranscriptomic and metagenomic studies [79] from the gill‐associated microbial diversity and surrounding hydrothermal vent sediments [80, 81] in view of the broader ecological organization and evolutionary importance of animal‐bacterial microbiomes in chemosynthetic‐based ecosystems in the deep sea [82, 83].

In recent years, researchers have turned to the human microbiome for its functional role in human health [84] and both composition and alterations in the microbiome have been found associated with diabetes, inflammatory bowel disease, obesity, asthma, rheumatoid arthritis, and susceptibility to infections [85]. Other microbiomes from nonmammalian and nonvertebrate species have also been characterized, for instance in insects where it was found to be highly dependent on the environment, species, and populations and affecting the fitness of species. These fitness effects may have important implications for the conservation and management of species and populations [82, 83]. Given the temporal instability of deep‐sea hydrothermal vents and their constant fluctuations of physical and chemical environmental conditions, vent animal‐microbiome associations have become critical for our understanding of invasion of nonnative species, responses to pathogens, and responses to chemicals and global climate change in the present and future [82] particularly when deep‐sea mining activities are projected to have a major impact on deep‐sea vent ecosystems [86].

Advertisement

Acknowledgments

Acknowledgements are due to IMAR—Marine Institute, Research and Development Unit #531 in the Azores (Thematic Area E) and Portuguese Fundação para a Ciência e Tecnologia (FCT) through the funding program FCOMP‐01‐0124‐FEDER‐007376 and the pluri‐annual and programmatic funding schemes—OE‐FEDER‐POCI2001‐FSE and PEst project—OE/EEI/LA0009/2011–2014. We also acknowledge the Regional Government of the Azores and Its Science and Technology Directorate through the pluri‐annual funding scheme and its funding support through the Operational Program PROCONVERGENCIA 2007‐20013 under the auspices of the European Union Regional strategic fund FEDER and through the research grant IBBA M2.1.2/I/029/2008‐BioDeepSea awarded to RB. The Luso‐American Foundation FLAD research grants project 600‐08/2016 and project L‐V‐173/2006; the Fulbright Commission through the Fulbright Research Scholar grant awarded to RB (2005‐2006) are also acknowledged. This work also received the support from the Fundação para a Ciência e Tecnologia, through the strategic research fund UID/MAR/04292/2013 granted to MARE‐Marine and Environmental Sciences Centre; through the research grant IMUNOVENT PTDC/MAR/65991/2006 awarded to RB; through the research grants DEEPFUN‐PTDC/MAR/111749/2009 and FCOMP‐OE/EEI/LA0009/2011) awarded to AC; through the post‐doctoral scholarship SFRH/BDP/14896/2004 awarded to RB; through the post‐doctoral scholarship SFRH/BPD/73481/2010 awarded to IM; through the doctoral scholarships SFRH/BD/689511/2010, and EM SFRH/BD/73152/2010 awarded to EM and IB, respectively. The Azorean Science and Technology Directorate doctoral scholarship M3.1.2/F/052/2011 granted to TC is acknowledge. RB was also supported by Fundação para a Ciência e Tecnologia through CIÊNCIA‐2007 Research contract (2008‐2013). AC was supported by the Program Investigador FCT‐IF/00029/2014/CP1230/CT0002 from the Fundação para a Ciência e Tecnologia.

References

  1. 1. Corliss JB, Dymond J, Gordon LI, Edmond JM, von Herzen RP, et al. Submarine thermal springs on the Galapagos Rift. Science. 1979;203:1073-1083. DOI: 10.1126/science.203.4385.1073
  2. 2. Childress JJ, Fisher CR. The biology of hydrothermal vent animals: Physiology, biochemistry, and autotrophic symbioses. Oceanography and Marine Biology: An Annual Review. 1992;30:337-441. Aberdeen University Press/Allen & Unwin: London. ISSN 0078‐3218
  3. 3. Childress JJ. Are there physiological and biochemical adaptations of metabolism in deep‐sea animals? Trends in Ecology and Evolution. 1995;10(1):30-36. PMCID: PMC40849
  4. 4. Van Dover CL. The Ecology of Deep‐Sea Hydrothermal Vents. Princeton, NJ: Princeton University Press; 2000. ISBN: 9780691049298
  5. 5. Salerno JL, Macko SA, Hallam SJ, Bright M, Won YJ, McKiness Z, Van Dover CL. Characterization of symbiont populations in life‐history stages of mussels from chemosynthetic environments. Biological Bulletin. 2005;208:145-155.DOI:10.2307/3593123
  6. 6. Cavanaugh CM, McKiness ZP, Newton IL, Stewart FJ. Marine chemosynthetic symbioses. In: The Prokaryotes. New York: Springer; 2006. pp. 475-507
  7. 7. Dubilier N, Bergin C, Lott C. Symbiotic diversity in marine animals: The art of harnessing chemosynthesis. Nature Reviews Microbiology. 2008;6:725-740.DOI:10.1038/nrmicro1992
  8. 8. Duperron S, Lorion J, Samadi S, Gros O, Gaill F. Symbioses between deep‐sea mussels (Mytilidae: Bathymodiolinae) and chemosynthetic bacteria: Diversity, function and evolution. Comptes Rendues Biologies. 2009;332:298-310. DOI:10.1016/j.crvi.2008.08.003
  9. 9. Von Cosel R, Comtet T, Krylova EM. Bathymodiolus (Bivalvia: Mytilidae) from hydrothermal vents on the Azores triple junction and the Logatchev hydrothermal field, Mid Atlantic Ridge. Veliger. 1999;42:218-248. biostor/129413
  10. 10. Distel DL, Lee HKW, Cavanaugh CM. Intracellular coexistence of methanotrophic and thioautotrophic bacteria in a hydrothermal vent mussel. Proceedings of the National Academy of Sciences of the United States of America. 1995;92:9598-9602. PMCID: PMC40849
  11. 11. Fiala‐Medioni A, McKiness ZP, Dando P, Boulegue J, Mariotti A, Alayse‐Danet AM, Robinson JJ, Cavanaugh CM. Ultrastructural, biochemical, and immunological characterization of two populations of the mytilid mussel Bathymodiolus azoricus from the Mid‐Atlantic Ridge: Evidence for a dual symbiosis. Marine Biology. 2002;141:1035-1043
  12. 12. Duperron S, Bergin C, Zielinski F, Blazejak A, Pernthaler A, McKiness ZP, DeChaine E, Cavanaugh CM, Dubilier N. A dual symbiosis shared by two mussel species, Bathymodiolus azoricus and Bathymodiolus puteoserpentis (Bivalvia: Mytilidae), from hydrothermal vents along the northern Mid‐Atlantic Ridge. Environmental Microbiology. 2006;8:1441-1447. DOI: 10.1111/j.1462‐2920.2006.01038
  13. 13. Duperron S, Gaudron SM, Rodrigues CF, Cunha MR, Decker C, Olu K. An overview of chemosynthetic symbioses in bivalves from the North Atlantic and Mediterranean Sea. Biogeosciences. 2013;10:3241-3267. DOI: 10.5194/bg‐10‐3241‐2013
  14. 14. Charlou JL, Donval JP, et al. Compared geochemical signatures and the evolution of Menez Gwen (37°50’N) and Lucky Strike (37°17’N) hydrothermal fluids, south of the Azores Triple Junction on the Mid‐Atlantic Ridge. Chemical Geology. 2000;171:49-75
  15. 15. Fisher CR, Brooks JM, Childress JJ, Felbeck H, Hessler RR, Johnson KS, Macko SA, Moe A, Nelson D, Somero GN. Microhabitat requirements of the hydrothermal vent mussel, Bathymodiolus thermophilus. American Zoology. 1989;29:A81. DOI: http://dx.doi.org/10.1016/0198‐0149(88)90049‐0
  16. 16. Desbruyères D, Almeida A, Biscoito M, Comtet T, Khripounoff A, Le Bris N, Sarradin PM, Segonzac M. A review of the distribution of hydrothermal vent communities along the northern Mid‐Atlantic Ridge: Dispersal vs. Environmental controls. Hydrobiologia. 2000;400:201-216. DOI: 10.1023/A:1004175211848
  17. 17. Desbruyères D, Biscoito M, Caprais JC, Colaço A, Comtet T, Crassous Ph, Fouquet Y, Khripounoff A, Le Bris N, Olu K, Riso R, Sarradin PM, Segonzac M, Vangriesheim A. Variations in deep‐sea hydrothermal vent communities on the Mid‐Atlantic Ridge near the Azores plateau. Deep Sea Research Part I. 2001;48:1325-1346. DOI: http://dx.doi.org/10.1016/S0967‐0637(00)00083‐2
  18. 18. Bettencourt R, Roch P, Stefanni S, Rosa D, Colaço A, Serrão Santos R. Deep sea immunity: Unveiling immune constituents from the hydrothermal vent mussel Bathymodiolus azoricus. Marine Environmental Research. 64:108-127. DOI: 10.1016/j.marenvres.2006.12.010
  19. 19. Bettencourt R, Dando P, Collins P, Costa V, Allam B, Serrão Santos R. Innate immunity in the deep‐sea hydrothermal vent mussel Bathymodiolus azoricus. Comparative Biochemistry and Physiology Part A: Molecular & Integrative Physiology. 2009;152:278-289. DOI: http://dx.doi.org/10.1016/j.cbpa.2008.10.022
  20. 20. Bettencourt R, Dando P, Rosa D, Riou V, Colaço A, Sarrazin J, Sarradin PM, Serrão Santos R. Changes of gill and hemocyte‐related bio‐indicators during long termmaintenance of the vent mussel Bathymodiolus azoricus held in aquaria at atmospheric pressure. Comparative Biochemistry and Physiology Part A. 2008;150:1-7. DOI: 10.1016/j.cbpa.2008.02.020
  21. 21. Bettencourt R, Costa V, Laranjo M, Rosa D, Pires L, Colaco A, Lopes H, Serrao Santos R. Out of the deep‐sea into a land‐based aquarium environment: Investigating physiological adaptations in the hydrothermal vent mussel Bathymodiolus azoricus. ICES Journal of Marine Science. 2011;68(2):357-364. DOI: 10.1093/icesjms/fsq119
  22. 22. Bettencourt R, Costa V, Laranjo M, Rosa D, Pires L, Colaco A, Sarradin Pierre M, Lopes H, Sarrazin Marie J, Santos Serrao R. Out of the deep‐sea into a land‐based aquarium environment: Investigating innate immunity in the hydrothermal vent mussel Bathymodiolus azoricus. Cahiers De Biologie Marine. 2010;51(4):341-350. DOI: http://archimer.ifremer.fr/doc/00019/13042/
  23. 23. Colaco A,Bettencourt R, Costa V, Lino S, Lopes H, Martins I, Pires L,, Prieto C, Serrão Santos R. LabHorta: A controlled aquarium system for monitoring physiological characteristics of the hydrothermal vent mussel Bathymodiolus azoricus. ICES Proceedings ICES Journal of Marine Science. 2011;68(2):349-356. DOI: 10.1093/icesjms/fsq120
  24. 24. Kadar E, Bettencourt R, Costa V, Santos RS, Lobo‐Da‐Cunha A, Dando P. Experimentally induced endosymbiont loss and re‐acquirement in the hydrothermal vent bivalve Bathymodiolus azoricus. Journal of Experimental Marine Biology and Ecology. 2005;318:99-110. DOI: 10.1016/j.jembe.2004.12.025
  25. 25. Kadar E, Powell JJ. Post‐capture experimental investigations using hydrothermal vent macro‐invertebrates to study adaptations to extreme environments. Reviews in Environmental Science and Bio/Technology. 2006;5:193-201. DOI: 10.1007/ 978‐1‐40 20‐6 285‐8_18
  26. 26. Martins I, Romão CV, Goulart J, Cerqueira T, Santos RS, Bettencourt R. Activity of antioxidant enzymes in response to atmospheric pressure induced physiological stress in deep‐sea hydrothermal vent mussel Bathymodiolus azoricus. Marine Environmental Research. 2016;114:65-73. DOI: 10.1016/j.marenvres.2016.01.003
  27. 27. Canesi L, Pruzzo C. Specificity of innate immunity in bivalves: A lesson from Bacteria. In: Ballarin L, Cammarata M, editors. Lessons in Immunity: From Single‐Cell Organisms to Mammals. Academic Press; Elsevier Inc; 2016. ISBN: 978‐0‐12‐803252
  28. 28. Allam B, Raftos D. Immune responses to infectious diseases in bivalves. Journal of Invertebrate Pathology. 2015;131:121-136. DOI: 10.1016/j.jip.2015.05.005
  29. 29. Song L, Wang L, Zhang H, Wang M. The immune system and its modulation mechanism in scallop. Fish and Shellfish Immunology. 2015;46(1):65-78. DOI: 10.1016/j.fsi.2015.03.013
  30. 30. Gerdol M, Venier P. An updated molecular basis for mussel immunity. Fish and Shellfish Immunology. 2015;46(1):17-38. DOI: 10.1016/j.fsi.2015.02.013
  31. 31. Richard G, Guérard F, Corporeau C, Lambert C, Paillard C, Pernet F. Metabolic responses of clam Ruditapes philippinarum exposed to its pathogen Vibrio tapetis in relation to diet. Developmental Comparative Immunology. 2016;60:96-107. DOI: 10.1016/j.dci.2016.02.026
  32. 32. Wang Q, Cao R, Ning X, You L, Mu C, Wang C, Wei L, Cong M, Wu H, Zhao J. Effects of ocean acidification on immune responses of the Pacific oyster Crassostrea gigas. Fish and Shellfish Immunology. 2016;49:24-33. DOI: 10.1016/j.fsi.2015.12.025
  33. 33. Ben Cheikh Y, Travers MA, Morga B, Godfrin Y, Rioult D, Le Foll F. First evidence for a Vibrio strain pathogenic to Mytilus edulis altering hemocyte immune capacities. Developmental & Comparative Immunology. 2016;57:107-119. DOI: 10.1016/j.dci.2015.12.014
  34. 34. Donaghy L, Lambert C, Choi KS, Soudant P. Hemocytes of the carpet shell clam (Ruditapes decussatus) and the Manila clam (Ruditapes philippinarum): Current knowledge and future prospects. Aquaculture. 2009;297:10-24. <hal‐00460793>
  35. 35. Wootton EC, Dyrynda EA, Ratcliffe NA. Bivalve immunity: Comparisons between the marine Mussel (Mytilus edulis), the edible cockle (Cerastoderma edule) and the razor Shell (Ensis siliqua). Fish and Shellfish Immunology. 2003;15(3):195-210
  36. 36. Allam B, Ashton‐Alcox A, Ford SE, Flow cytometric measurement of haemocyte viability and phagocytic activity in the clam, Ruditapes philippinarum. Journal of Shellfish Research. 2002;21:13-19
  37. 37. Allam B, Paillard C, Ford SE. Pathogenicity of Vibrio tapetis, the etiological agent of brown ring disease (BRD) in clams. Diseases of Aquatic Organisms. 2002;48:221-231
  38. 38. Canesi L, Gallo G, Gavioli M, Pruzzo C. Bacteria‐hemocyte interactions and phagocytosis in marine bivalves. Microscopy and Research Technique Journal. 2002;57(6):469-476
  39. 39. Ciacci C, Citterio B, Betti M, Canonico B, Roch P, Canesi L. Functional differential immune responses of Mytilus gallorpovincialis to bacterial challenge. Comparative Biochemistry and Physiology Part B: Biochemistry and Molecular Biology. 2009;153(4):365-371
  40. 40. Takeuchi O, Akira S. Pattern recognition receptors and inflammation. Cell. 2010;140(6): 805-820. DOI: 10.1016/j.cell.2010.01.022
  41. 41. Vance RE, Isberg RR, Portnoy DA. Patterns of pathogenesis: Discrimination of pathogenic and nonpathogenic microbes by the innate immune system. Cell Host & Microbe. 2009;6. DOI: 10.1016/j.chom.2009.06.007
  42. 42. Zuykov M, Pelletier E, Harper DAT. Bivalve mollusks in metal pollution studies: From bioaccumulation to biomonitoring. Chemosphere. 2013;93(2):201-208
  43. 43. El‐Sikaily A, Khaled A, El Nemr A. Heavy metals monitoring using bivalves from Mediterranean sea and Red sea. Environmental Monitoring and Assessment. 2004;98(1): 41-58
  44. 44. Spada L, Annicciarico C, Cardellicchio N, Giandomenico S, Di Leo A. Heavy metals monitoring in the mussel Mytilus galloprovincialis from the Apulian coast (Southern Italy). Mediterranean Marine Science. 2013;14(1):99-108
  45. 45. Martins I, Cosson RP, Riou V, Sarradin P‐M, Sarrazin J, Santos Serrão R, Colaço A. Relationship between metal levels in the vent mussel Bathymodiolus azoricus and local microhabitat chemical characteristics of Eiffel Tower (Lucky Strike). Deep Sea Research Part I: Oceanographic Research Papers. 2011;58(3):306-315. DOI: 10.1016/j.dsr.2011.01.002
  46. 46. Cosson RP, Thiébaut E, Company R, Castrec‐Rouelle M, Colaço A, Martins I, Sarradin PM, Bebianno MJ. Spatial variation of metal bioaccumulation in the hydrothermal vent mussel Bathymodiolus azoricus. Marine Environmental Research. 2008;65(5):405-415. DOI: 10.1016/j.marenvres. 2008.01.005
  47. 47. Lino AS, Galvão PMA, Longo RTL, Azevedo‐Silva CE, Dorneles PR, Torres JPM, Malm O. Metal bioaccumulation in consumed marine bivalves in Southeast Brazilian coast. Journal of Trace Elements in Medicine and Biology. 2016;34:50-55. http://dx.doi.org/10.1016/j.jtemb.2015.12.004
  48. 48. Chu H, Mazmanian SK. Innate immune recognition of the microbiota promotes host microbial symbiosis. Nature Immunology. 2013;14(7):668-675. DOI:10.1038/ni.2635
  49. 49. Littman DR, Pamer EG. Role of the commensal microbiota in normal and pathogenic host immune responses. Cell Host Microbe. 2011;10(4):311-323. DOI: 10.1016/j.chom.2011.10.004
  50. 50. Bettencourt R, Pinheiro M, Egas C, Gomes P, Afonso M, Shank T, Santos RS. High‐throughput sequencing and analysis of the gill tissue transcriptome from the deep‐sea hydrothermal vent mussel Bathymodiolus azoricus. BMC Genomics. 2010;11:559. DOI: 10.1186/1471‐2164‐11‐559
  51. 51. Shillito B, Jollivet D, Sarradin P, Rodier P, Lallier F, et al. Temperature resistance of Hesiolyra bergi, a polychaetous annelid living on deep‐sea vent smoker walls. Marine Ecology Progress Series. 2001;216:141-149. DOI: http://archimer.ifremer.fr/doc/00000/811/
  52. 52. Riou V, Halary S, Duperron S, Bouillon S, Elskens M, Bettencourt R, Santos RS, Dehairs F, Colaço A. Influence of CH4 and H2S availability on symbiont distribution, carbon assimilation and transfer in the dual symbiotic vent mussel Bathymodiolus azoricus. Biogeosciences. 2008;5:1681-1691. DOI:10.5194/bg‐5‐1681‐2008
  53. 53. Martins E, Queiroz A, Serrão Santos R, Bettencourt R. Finding immune gene expression differences induced by marine bacterial pathogens in the Deep‐sea hydrothermal vent mussel Bathymodiolus azoricus. Biogeosciences. 2013;10(11):7279-7291. DOI: 10.5194/bg‐10‐7279‐2013
  54. 54. Martins E, Figueras A, Novoa B, Serrão Santos R, Moreira R, Bettencourt R. Comparative study of immune responses in the Deep‐sea hydrothermal vent mussel Bathymodiolus azoricus and the Shallow‐water mussel Mytilus galloprovincialis challenged with Vibrio bacteria. Fish and Shellfish Immunology. 2014;40(2):485-499. DOI: 10.1016/j.fsi.2014.07.018
  55. 55. Martins E, Serrão Santos R, Bettencourt R. Vibrio diabolicus challenge in Bathymodiolus azoricus populations from Menez Gwen and Lucky Strike hydrothermal vent sites. Fish Shellfish Immunology. 2015;47:962-977. DOI: http://dx.doi.org/10.1016/j.fsi.2015.10.038
  56. 56. Barros I, Divya B, Martins I, Vandeperre F, Santos RS, et al. Post‐capture immune gene expression studies in the deep‐sea hydrothermal vent mussel Bathymodiolus azoricus acclimatized to atmospheric pressure. Fish Shellfish Immunology. 2014;42:159-170. DOI: 10.1016/j.fsi.2014.10.018
  57. 57. Boutet I, Jollivet D, Shillito B, Moraga D, Tanguy A. Molecular identification of differentially regulated genes in the hydrothermal‐vent species Bathymodiolus thermophilus and Paralvinella pandorae in response to temperature. BMC Genomics. 2009;10:222
  58. 58. Boutet I, Ripp R, Lecompte O, Dossat C, Corre E, Tanguy A, Lallier FH. Conjugating effects of symbionts and environmental factors on gene expression in deep‐sea hydrothermal vent mussels. BMC Genomics. 2011;12:530. DOI: 10.1186/1471‐2164‐12‐530
  59. 59. Wang Z, Gerstein M, Snyder M. RNA‐Seq: A revolutionary tool for transcriptomics. Nature Reviews Genetics. 2009;10(1):57-63. DOI: 10.1038/nrg2484
  60. 60. Wall PK, et al. Comparison of next generation sequencing technologies for transcriptome characterization. BMC Genomics. 2009;10:347. DOI: 10.1186/1471‐2164‐10‐347
  61. 61. Hahn DA, Ragland GJ, Shoemaker DW, Denlinger DL. Gene discovery using massively parallel pyrosequencing to develop ESTs for the flesh fly Sarcophaga crassipalpis. BMC Genomics. 2009;10:234. DOI: 10.1186/1471‐2164‐10‐234
  62. 62. Emrich SJ, Barbazuk WB, Li L, Schnable PS. Gene discovery and annotation using LCM‐454 transcriptome sequencing. Genome Research. 2007;(1):69-73
  63. 63. Jarvie T, Harkins T. Transcriptome sequencing with the genome sequencer FLX system. Nature Methods. 2007;4
  64. 64. Grabherr MG, et al. Full‐length transcriptome assembly from RNA‐seq data without a reference genome. Nature Biotechnology. 2011;29(7):644-652. DOI: 10.1038/nbt.1883
  65. 65. Chen Y, Lun ATL, Smyth GK. From reads to genes to pathways: Differential expression analysis of RNA‐Seq experiments using Rsubread and the edgeR quasi‐likelihood pipeline. F1000Research. 2016;5:1438
  66. 66. Brown ]Stuart M. Sequencing‐by‐Synthesis: Explaining the Illumina Sequencing Technology [Internet] 2012. Available from: http://bitesizebio.com/13546/sequencing‐by‐synthesis‐explaining‐the‐illumina‐sequencing‐technology/ [Accessed: August 30, 2012]
  67. 67. Hass BJ, et al. De novo transcript sequence reconstruction from RNA‐seq using the Trinity platform for reference generation and analysis. Nature Protocols. 2013;8:1494-1512. DOI: 10.1038/nprot.2013.084
  68. 68. Robinson MD, McCarthy DJ, Smyth GK. edgeR: A bioconductor package for differential expression analysis of digital gene expression data. Bioinformatics. 2010;26(1):139-140
  69. 69. http://trinityrnaseq.sourceforge.net/analysis/diff_expression_analysis.html
  70. 70. http://manuals.bioinformatics.ucr.edu/home/R_BioCondManual
  71. 71. Egas C, Pinheiro M, Gomes P, Barroso C, Bettencourt R. The transcriptome of Bathymodiolus azoricus gill reveals expression of genes from endosymbionts and free‐living deep‐sea bacteria. Marine Drugs. 2012;10:1765-1783. DOI: 10.3390/md10081765
  72. 72. Bettencourt R, Rodrigues M, Barros I, Cerqueira T, Freitas C, Costa V, Pinheiro M, Egas C, Serrão Santos R. Site‐related differences in gene expression and bacterial densities in the mussel Bathymodiolus azoricus from the Menez Gwen and Lucky Strike deep‐sea hydrothermal vent sites. Fish and Shellfish Immunology. 2014;39(2):343-353. DOI: 10.1016/j.fsi.2014.05.024
  73. 73. Duperron S, Nadalig T, Caprais J‐C, Sibuet M, Fiala‐Médioni A, Rudolf A, Dubilier N. Dual symbiosis in a Bathymodiolus sp. mussel from a methane seep on the Gabon continental margin (Southeast Atlantic): 16S rRNA phylogeny and distribution of the symbionts in gills. Applied and Environmental Microbiology. 2005;71(4):1694-1700
  74. 74. Barros I, Mendes S, Rosa D, Serrão Santos R, Bettencourt R. Vibrio diabolicus immunomodulatory effects on Bathymodiolus azoricus during long‐term acclimatization at atmospheric pressure. Journal of Aquaculture and Development. 2016,7:12 DOI: 10.4172/2155‐9546.1000464
  75. 75. Kawai T, Akira S. Signaling to NF‐kB by Toll‐like receptors. Trends in Molecular Medicine. 2007;13(11). DOI: 10.1016/j.molmed.2007.09.002
  76. 76. Toubiana M, Rosani U, Giambelluca S, Cammarata M, Gerdol M, Pallavicini A, Venier P, Roch P. Toll signal transduction pathway in bivalves: Complete cds of intermediate elements and related gene transcription levels in hemocytes of immune stimulated Mytilus galloprovincialis. Developmental Comparative Immunology. 2014;45(2):300-312. DOI: 10.1016/j.dci.2014.03.021
  77. 77. Canesi L, Ciacci C, Bergami E, Monopoli MP, Dawson KA, Papa S, Canonico B, Corsi I. Evidence for immunomodulation and apoptotic processes induced by cationic polystyrene nanoparticles in the hemocytes of the marine bivalve Mytilus. Marine Environmental Research. 2015;111:34-40. DOI: 10.1016/j.marenvres.2015.06.008
  78. 78. Schmidt W, Power E, Quinn B. Seasonal variations of biomarker responses in the marine blue mussel (Mytilus spp). Marine Pollution Bulletin. 2013;74(1):50-55. DOI: 10.1016/j.marpolbul.2013.07.033
  79. 79. Simon C, Daniel R. Metagenomic analyses: Past and future trend. Applied and Environmental Microbiology.2011;77(4):1153-1161. DOI: 10.1128/AEM.02345‐10
  80. 80. Cerqueira T, Pinho D, Egas C,Froufe H, Altermark B, Candeias C, Santos RS, Bettencourt R. Microbial diversity in deep‐sea sediments from the Menez Gwen hydrothermal vent system of the Mid‐Atlantic Ridge. Marine Genomics. 2015. DOI: 10.1016/j.margen.2015.09.001
  81. 81. Cerqueira T, Pinho D, Froufe H, Serrão Santos R, Bettencourt R, Egas C. Sediment microbial diversity of three deep‐sea hydrothermal vents southwest of the Azores. Microbial Ecology. 2017. DOI 10.1007/s00248‐017‐0943‐9
  82. 82. Christian N, Whitaker BK, Clay, K. Microbiomes: Unifying animal and plant systems through the lens of community ecology theory. Frontiers in Microbiology. 2015;6:869. DOI: 10.3389/fmicb.2015.00869
  83. 83. Bahrndorff S, Alemu T, Alemneh T, Lund Nielsen J. The microbiome of animals: Implications for conservation biology. International Journal of Genomics. 2016; 5304028. DOI: 10.1155/2016/5304028
  84. 84. Turnbaugh PJ, Ley RE, Hamady M, Fraser‐Liggett CM, Knight R, Gordon JI. The human microbiome project. Nature. 2007;449(7164):804-810. DOI: 10.1038/nature06244
  85. 85. Cho I, Blaser MJ. The human microbiome: At the interface of heath and disease. Nature Reviews Genetics. 2012;13(4):260-270. DOI: 10.1038/nrg3182
  86. 86. Van Dover CL. Impacts of anthropogenic disturbances at deep‐sea hydrothermal vent ecoystems: A review. Marine Environmental Research. 2014;102:59-72. DOI: 10.1016/j.marenvres.2014.03.008

Written By

Raul Bettencourt, Inês Barros, Eva Martins, Inês Martins, Teresa Cerqueira, Ana Colaço, Valentina Costa, Domitília Rosa, Hugo Froufe, Conceição Egas, Sergio Stefanni, Paul Dando and Ricardo S. Santos

Submitted: 10 November 2016 Reviewed: 21 February 2017 Published: 16 August 2017