Abstract
Coastal areas form the major habitat of brown macroalgae, photosynthetic multicellular eukaryotes that have great ecological value and industrial potential. Macroalgal growth, development, and physiology are influenced by the microbial community they accommodate. Studying the algal microbiome should thus increase our fundamental understanding of algal biology and may help to improve culturing efforts. Currently, a freshwater strain of the brown macroalga Ectocarpus subulatus is being developed as a model organism for brown macroalgal physiology and algal microbiome studies. It can grow in high and low salinities depending on which microbes it hosts. However, the molecular mechanisms involved in this process are still unclear. Cultivation of Ectocarpus-associated bacteria is the first step toward the development of a model system for in vitro functional studies of brown macroalgal–bacterial interactions during abiotic stress. The main aim of the present study is thus to provide an extensive collection of cultivable E. subulatus-associated bacteria. To meet the variety of metabolic demands of Ectocarpus-associated bacteria, several isolation techniques were applied, i.e., direct plating and dilution-to-extinction cultivation techniques, each with chemically defined and undefined bacterial growth media. Algal tissue and algal growth media were directly used as inoculum, or they were pretreated with antibiotics, by filtration, or by digestion of algal cell walls. In total, 388 isolates were identified falling into 33 genera (46 distinct strains), of which Halomonas (Gammaproteobacteria), Bosea (Alphaproteobacteria), and Limnobacter (Betaproteobacteria) were the most abundant. Comparisons with 16S rRNA gene metabarcoding data showed that culturability in this study was remarkably high (∼50%), although several cultivable strains were not detected or only present in extremely low abundance in the libraries. These undetected bacteria could be considered as part of the rare biosphere and they may form the basis for the temporal changes in the Ectocarpus microbiome.
Introduction
Coastal areas form the major habitat of brown macroalgae, photosynthetic eukaryotic organisms that are important primary producers and form biodiversity hotspots for other marine (macro)organisms by providing them with food and shelter (Thornber et al., 2016). The seaweed surface is a highly attractive substrate for the settlement of marine microorganisms, due to the fact that they actively excrete carbohydrates and other organic or growth-promoting substances (; ) that can be rapidly utilized by bacteria. Several stable relationships exist that have been shown to benefit brown macroalgal hosts (; ; ). Algae-associated (symbiotic) microbes can, for example, communicate on a chemical level through the provision of growth hormones (), vitamins (; ), or morphogens (Tapia et al., 2016), and some algal–bacterial interactions are known to affect biofouling and pathogenic invasion by other microorganisms (). Due to the tight relationships and functional co-dependencies between algae and their associated microbiomes, both can be seen as one functional entity or “holobiont" (Zilber-Rosenberg and Rosenberg, 2008; ).
Elucidating the functions and molecular mechanisms that shape the algal holobiont is of crucial importance, not only for the fundamental understanding of macroalgal functioning in marine ecosystems, but also to improve macroalgal culturing, an industry that has increased intensively over the last decade due to the growing interest in algae as a source for nutrients, chemicals, and bioactive compounds (Wells et al., 2017). In vitro studies of the commercially valuable and environmentally most relevant brown macroalgae (kelps, order Laminariales) remain challenging due to their size and complex life cycles (). Model organisms, such as the filamentous brown alga Ectocarpus are therefore an essential tool to enable functional studies on algal–bacterial interactions in the laboratory. Ectocarpus is easily cultivable in vitro, has a short life cycle and a relatively small genome which has been sequenced several years ago (; ).
Here, we study the microbiome of a freshwater strain of Ectocarpus subulatus (West and Kraft, 1996). The transition to fresh water is a rare event in brown algae that occurred in only a few species (). The examined strain is currently the only publicly available freshwater isolate within the Ectocarpales, and it is still able to grow in both seawater and freshwater (). This and other isolates of the same species are known for their particularly high tolerance to abiotic stressors (; ) and are being developed as a model to study brown algal adaptation and acclimation. These processes, and in particular algal growth in fresh water, have been shown to depend on interactions with symbiotic bacteria ().
The aim of the present study is to develop an extensive collection of cultivable E. subulatus-associated bacteria that can be used to study the functions of bacterial symbionts during abiotic stress in controllable and reproducible experimental settings, using the freshwater strain of E. subulatus as a model. Different bacterial isolation techniques were applied in parallel to increase the number and diversity of cultivable strains, i.e., direct plating and dilution-to-extinction cultivation techniques, each with chemically defined and undefined bacterial growth media. Algal tissue and algal growth media were directly used as inoculum, or they were pretreated with antibiotics, by filtration, or by digestion of algal cell walls. Our data show an overall high culturability of Ectocarpus-associated bacteria including a high number of low abundance taxa.
Materials and Methods
Cultivation of Algae – Starting Material for Isolation of Bacterial Symbionts
All experiments were carried out using sporophytes of the E. subulatus freshwater strain (EC371, accession CCAP 1310/196, West and Kraft, 1996). This culture was obtained from Bezhin Rosko (Santec, France) in 2007 and maintained in our laboratory under the following conditions since then: cultures of EC371 were grown in Petri dishes (90 mm Ø) in natural seawater (NSW; collected in Roscoff 48°46′40′′ N, 3°56′15′′ W, 0.45 μm filtered, autoclaved at 120°C for 20 min), or in diluted seawater-based medium (DNSW; by 20-fold dilution of natural seawater with distilled water). Both media were enriched with Provasoli nutrients (Starr and Zeikus, 1993) and cultures kept at 13°C with a 12 h dark-light cycle (photon flux density 20 μmol m-2 s-1).
Isolation and Characterization of Algae-Associated Bacteria
A range of cultivation strategies as well as bacterial growth media was exploited. The starting material for bacterial isolation was EC371 grown with its full microbial flora (direct plating and dilution-to-extinction cultivation) and EC371 with a reduced microbial flora (size-fractionation and antibiotic treatment), both originating from the same algal culture. Algal subcultures were sampled 5–10 days after the last change in medium. Algal growth medium and ground algal tissue, in NSW and DNSW were used. The isolation experiments took place from November 2013 to September 2016. Three selected cultivation experiments (dilution-to-extinction cultivation, direct plating with antibiotics; direct plating without pretreatment) were repeated under identical conditions after 6 months, 1 year, or 3 years, respectively, to assess reproducibility of the results over time. An overview of the isolation methods and cultivation strategies is provided in Figure 1.
FIGURE 1
Isolation of Bacteria from Algae with Their Full Microbial Flora
Direct plating techniques
To isolate bacteria, algal growth media, ground algal tissue, and algal protoplast digest product of EC371 grown in DNSW or NSW were directly plated (DP) on eight different growth media solidified with 1.5% agar. The eight bacterial growth media were: R2A prepared in distilled water (adapted from
Dilution-to-extinction cultivation
As a strategy to reduce nutrient competition between the cultivable members of the EC371 microbiome, the high throughput dilution-to-extinction (DTE) cultivation approach was used as originally described by
Isolation of Bacteria from Algae with a Reduced Microbial Flora
Size-fractionation of algal growth media
As a second strategy to reduce bacterial cell numbers before plating, size-fractionation (SF) was used to facilitate the growth of smaller and less abundant bacterial strains. EC371 culture medium was filtered with 0.2 (SF0.2), 0.45 (SF0.45), or 40 (SF40) μm pore-size, and 50 μl filtrate were directly plated on R2A or Zobell agar. At the same time, 100 μl filtrate were used to inoculate liquid R2A or Zobell as an intermediate to enhance bacterial growth before plating. After 5–8 days of incubation at RT, 50 μl of the liquid culture were plated on solidified R2A and/or Zobell. In both cases, plates were incubated until single colonies were visible (3–20 days) and the latter identified with 16S rRNA amplicon sequencing as described below.
Antibiotic-treatments of algal tissue and growth media
Antibiotics were used to reduce the abundance of dominant bacterial strains from the algal tissue and/or growth media, in our case especially Halomonas sp., and to facilitate the growth of other less abundant or slower-growing bacteria. Algal growth media and/or ground algal tissue was spread on R2A agar plates and incubated with two antibiotic disks (AbD1 and AbD2; Antimicrobial Susceptibility Disks, Bio-Rad Laboratories, Inc., France) for 5 days at RT, using antibiotics that were shown to be effective against Ectocarpus-derived Halomonas. Alternatively, algal subcultures of the same strain were treated with liquid antibiotics (AbL) for 3 days before plating on R2A or Zobell, whereafter 50 μl were plated on solidified R2A or Zobell. An overview of the antibiotics (disks and liquid) and their concentration can be found in Supplementary Table S2. Plates were incubated (3–20 days) until single colonies were visible and the latter identified with 16S rRNA amplicon sequencing as described below. Two experiments using antibiotic-treated algal tissue (AbD2 with chloramphenicol and erythromycin) were repeated after 1 year.
Bacterial Identification by 16S rRNA Gene Sequencing
To identify bacterial isolates, single colonies were grown in the corresponding liquid growth media until maximal density was reached. Approximately 50–100 μl of cultures were heated for 15 min at 95°C. Then the 16S rRNA gene was amplified using universal primers (8F 5′ AGAGTTTGATCCTGGCTCAG and 1492R 5′ GGTTACCTTGTTACGACTT from Weisburg et al., 1991) and the GoTaq polymerase in a PCR reaction with the following amplification conditions: 2 min 95°C; [1 min 95°C; 30 s 53°C; 3 min 72°C] 30 cycles; 5 min 72°C. In some cases a commercial kit was used to extract DNA (NucleoSpin® Tissue, Machery-Nagel; support protocol for bacteria). The PCR products were purified using ExoSAP (Affymetrix, Inc., Thermo Fisher Scientific) and sequenced with Sanger technology (BigDye Xterminator v3.1 cycle sequencing kit, Applied Biosystems®, Thermo Fisher Scientific). Only the forward primer 8F was used for the sequencing reaction. For classification and analyses of the sequences, RDP classifier (Wang et al., 2007) and BLAST1 against the NCBI nr and 16S rRNA gene databases were used and sequences classified at the genus level if possible. Sequences were aligned2 and checked manually to verify mismatches and to identify distinct strains within a genus (>99% identity). The 16S rRNA gene sequences from each distinct cultivable strain were aligned using MAFFT version 7 (
The numbers of sequences obtained per taxa were normalized against the total number of sequences obtained within the complete cultivation study. To assess cultivation biases statistically, the absolute abundances of cultivable isolates were analyzed in R (
16S rRNA Gene Metabarcoding
To estimate the proportion of cultivable bacteria in our algal cultures, the collection of bacterial isolates was compared with 16S rRNA gene libraries from the same algal culture used for our isolation experiments. These libraries served as a reference to assess the total microbiome, including cultivated and non-cultivated bacteria; they were not used to infer diversity per se. EC371 cultures were grown for 9 weeks in seawater-based culture medium (changed on a monthly basis, last 1 week prior to sampling). Algal tissue was filtered with sterile coffee filters, dried on a paper-towel, and snap-frozen in liquid nitrogen. Four technical replicates were pooled two by two. Total DNA was isolated (NucleoSpin® Plant II, Machery-Nagel; standard protocol) and purified with Clontech CHROMA SPINTM-1000+DEPC-H2O Columns. The V3–V4 region of the 16S rRNA gene was amplified and sequenced with Illumina MiSeq technology by MWG Eurofins Biotech (Ebersberg, Germany) using their proprietary protocol. The first preliminary quality control was done with FastQC3, and fastq_quality_trimmer from the FASTX Toolkit4 was used to quality-trim and filter the 568,100 reads (quality threshold 25; minimum read length 200). The resulting 553,896 sequences (2.5% removed) were analyzed with Mothur (V.1.38.0) according to the MiSeq Standard Operating Procedures5 (
Results
Isolation and Characterization of Algae-Associated Bacteria
Global Taxonomic Distribution of Cultivable Bacteria
16S rRNA gene sequences were obtained for 388 bacterial isolates and they were distributed among four phyla, 15 bacterial orders, 34 genera, and 46 taxonomically unique strains. Five genera encompassed more than one distinct strain (i.e., at least one verified mismatch in the 16S rRNA sequence): Limnobacter sp. (2), Moraxella sp. (2), Sphingomonas sp. (3), Bacillus sp. (8), and Roseovarius sp. (2). The most abundant phylum among the cultivable isolates was Proteobacteria, with 89% of all isolates and 26 unique strains belonging to this group. Within Proteobacteria, Alpha- and Betaproteobacteria accounted for 34 and 32% of the isolates, respectively. However, Betaproteobacteria comprised three unique strains, while Alphaproteobacteria comprised 16 unique strains in our experiments. 23% of proteobacterial isolates belonged to Gammaproteobacteria, covering seven unique strains. Bacteroidetes (4% of isolates), Firmicutes (4%), and Actinobacteria (3%) were cultivated less frequently compared to Proteobacteria. Despite their lower abundance, the three groups contribute considerably to the cultivable diversity, accounting for 20 out of 46 unique strains. The most abundant cultivable bacterial genera were Limnobacter (27% of all isolates), Halomonas (20%), and Bosea (9%). 80% of Limnobacter isolates were obtained from dilution-to-extinction cultivation experiments. Halomonas strains were predominantly cultivated using direct plating techniques and algae with full flora (84% of Halomonas isolates). For Bosea, most isolates (83%) originated from antibiotic-treated algae. An overview of all bacterial isolates characterized and their corresponding sequence abundances can be found in Figure 2 and Supplementary Table S3.
FIGURE 2

Heat-map of cultivation and metabarcoding data. The number of sequences was normalized and log(x+1)-transformed for each unique cultivable strain and each experimental treatment (DP, direct plating without pretreatment; AbD, DP with pretreatment with antibiotic disks; AbL, DP with pretreatment with liquid antibiotics; SF, DP with pretreatment by size-fractionation; DTE, dilution-to-extinction cultivation). A comparison is made with molecular data from 16S rRNA metabarcoding (META16-NSW = this study; META13-NSW and META13-DNSW = previous study by
Isolation of Bacteria from Algae with Their Full Microbial Flora
Direct plating of ground algae and algal protoplast extract (DP)
Direct plating of ground algal tissue and protoplast digest resulted in the isolation and characterization of 110 isolates corresponding to 17 strains of which seven were uniquely isolated with this method. The most frequently isolated strain was Halomonas sp., a gammaproteobacterium that makes up for 58% of isolates obtained with this method. Isolates of this strain originated predominantly from ground algal tissue rather than algal growth medium (p = 1.92E-13). After Halomonas, Sphingopyxis (10%), and Hyphomonas (8%) were the most frequently isolated taxa. Four isolates originated from protoplast extracts: Imperialibacter sp. (two isolates), Sphingomonas sp. (one isolate), and Plantibacter sp. (one isolate). Direct plating of algal tissue was repeated after 3 years and Halomonas sp. was again the most frequently isolated strain (9 out of 12 isolates). Sphingomonas 2, and Plantibacter sp. were two protoplast-specific strains obtained using DP, but they were only isolated once in the experiment.
Dilution-to-extinction cultivation (DTE)
One hundred and fifty isolates were identified and 16S rRNA gene sequences revealed eight unique strains. There were no isolates that were specific for the origin of the starting material used (protoplast extract or spent algal growth medium). The most abundant isolates belonged to the genus Limnobacter (55% of isolates), suggesting that they were the most abundant cultivable bacterium in the original algal cultures. Furthermore, five unique strains (Brevundimonas, Erythrobacter, Hoeflea, Ahrensia, and Roseovarius 1) were exclusively found with dilution-to-extinction cultivation. Brevundimonas sp. was significantly more isolated from algal growth media (p = 0.00045) compared to algal tissue/protoplast extract (Supplementary Table S3). In addition, some Hyphomonas sp. and Undibacterium sp. strains were isolated but they were not exclusive for this method. Experiments were performed twice in a 6-month interval (DTE1 and DTE2), and Limnobacter was, in both experiments, the most frequently isolated taxon. The ratio of cultivable to total bacteria (estimated culturability) in the experiment varied from 44 to 68%, with different culturability dependent on the type of bacterial growth medium applied. DTE statistics and the Poisson calculations can be found in Table 1.
Table 1
| Experiment | Type of inoculation | Bacterial growth medium | # Bacterial cells inoculated (ntotal) | # Inoculated wells (w) | # Negative wells (Pneg) | Theoretical # of cultivable cells (ncult) | Estimated culturability (ncult/ntotal) |
|---|---|---|---|---|---|---|---|
| DTE1 | P | ECM 2W | 52 | 104 | 74 | 35.39 | 68% |
| DTE1 | P | ECM 7W | 52 | 104 | 83 | 23.46 | 45% |
| DTE1 | M | ECM 7W | 48 | 96 | 73 | 26.29 | 55% |
| DTE1 | M | ECM 2W | 48 | 96 | 77 | 21.17 | 44% |
| DTE1 | M | LNHM | 52 | 104 | 81 | 25.99 | 50% |
| DTE1 | M | 1:20 R2A | 52 | 104 | 79 | 28.59 | 55% |
| DTE2 | M | 1:20 R2A | 140 | 280 | 201 | 92.82 | 66% |
Estimation of the ratio of cultivable to total bacteria in the dilution-to-extinction cultivation experiments based on a Poisson distribution: ncult = ln(1/pneg)∗w.
P = protoplast digest product; M = low salinity algal growth medium; DTE1 = March 2016; DTE2 = September 2016; ECM = spent low salinity algal growth medium from 2 weeks (2W) or 7 weeks (7W) old cultures.
Isolation of Bacteria from Algae with Reduced Flora
Antibiotic-treated algae
The 16S rRNA gene sequences from 80 isolates revealed 27 unique strains, 16 of which were obtained only with this cultivation method. Bosea was the most abundant (44% of isolates) followed by Halomonas with 38%. Most others were only isolated once or twice. Unique strains isolated with this method were Sphingomonas sp. (strains 1, 3), Bacillus sp. (strains 1, 3–5, 7), Nocardioides sp., Microcella sp., Moraxella sp. (strains 1, 2), Pantoea sp., Rhizobium sp., two unclassified members of the Flavobacteriaceae, and Oceanicaulis sp. These were all (except Microcella) isolated from algal tissue that was exposed to 10 different antibiotics (Supplementary Table S2). The cultivation of bacteria from antibiotic-treated algae was performed twice within a 1-year interval and in both experiments Bosea was the most frequently isolated taxon.
Size-fractionation
The 16S rRNA gene sequences of the 43 isolates from this experiment cover 14 unique strains. Three of them were uniquely found using this method: Bacillus strain 6 (one isolate), Limnobacter strain 2, (two isolates), and Stenotrophomonas sp. (one isolate). Among the other strains cultivated, the most abundant one was Limnobacter strain 1 (40% of isolates), followed by Imperialibacter sp. (16% of isolates).
Estimating the Proportion of Cultivable Bacteria in Ectocarpus Cultures
16S metabarcoding experiments were carried out with the same algal culture also used for the isolation of bacteria and the libraries were used as a reference for the cultivated and non-cultivated microbiome as a whole. After cleaning and filtering of the data, the sequences were clustered into 48 OTUs. The most abundant OTU belonged to the genus Alteromonas (OTU1) and accounted for 41.6% of the reads, which makes Gammaproteobacteria the most abundant class (42.3%). Other abundant OTUs corresponded to an unclassified Rhodobacteraceae (OTU3, 11%) and an unclassified Bacteroidetes (OTU4, 10%). Together these three OTUs correspond to 62% of all sequences (Figure 3A). Alphaproteobacteria make up 32.8% of the sequences and Bacteroidetes 15.3% (Figure 3B). Other phyla identified are Actinobacteria (2.1%) and Deltaproteobacteria (7.5%). Of the 48 OTUs, 10 corresponded to strains cultivated in our experiments. These 10 OTUs accounted for 47% of the reads in the metabarcoding data. Purely based on absence/presence of OTUs the culturability was 21%. Three additional cultivable strains corresponded to OTUs with sequence abundance below the threshold (n ≤ 5, Staphylococcus, Hyphomonas, Oceanicaulis;Figure 3). Furthermore, taking into account all 16S rRNA gene libraries and rare reads, 22 of the 46 cultivable strains were detected. Among the 24 undetected strains that were not found in any of the barcoding libraries, 11 were isolated exclusively from DNSW and 8 exclusively from NSW. In the same vein, 11 strains were cultured exclusively from algal medium, and 7 only from algal tissue (Supplementary Table S4).
FIGURE 3

Overview of metabarcoding data and comparison with cultivable isolates. (A) Shows the distribution of OTUs in the metabarcoding experiment (META16-NSW). OTUs with >1% of total sequence abundance are displayed separately: bars in green display OTUs that correspond to cultivable strains obtained in this study, while purple bars correspond to OTUs that were not cultivated; OTUs with <1% of total sequence abundance are combined and the sum of sequences is displayed. (B) Shows the distribution of 16S rRNA gene metabarcoding sequences per phylum compared to data obtained from the cultivation study. (C) Shows a Venn-diagram of the OTUs that are shared between the 2 metabarcoding datasets from 2013 to 2016 and the cultivable isolates. Numbers in blue correspond to META16-NSW, numbers in red correspond to META2013-NSW, numbers in green to META2013-DNSW, and numbers in gray correspond to the proportion of sequences for cultivable isolates.
The 16S rRNA gene metabarcoding data obtained in this study (META2016-NSW) differed strongly from that obtained 3 years earlier (META2013-NSW) from the same Ectocarpus strain. Several OTUs that were present in the 2013 samples were no longer present in 2016 or declined in abundance below the detection limit. However, there were still 50 OTUs (corresponding to 90% of the sequences) shared between the 2013 and 2016 samples. The most abundant OTU in 2013 belonged to the genus Hoeflea (29% of reads) while the most abundant OTU in 2016 (Alteromonas sp.; 42% of reads) accounted for only 2.4% of the reads in 2013.
Discussion
Global Taxonomic Distribution of Cultivable Bacteria
The main aim of this study was to establish a diverse collection of cultivable Ectocarpus-associated bacteria that can be used to perform functional studies of brown macroalgal–bacterial interactions in this model organism. We applied different cultivation strategies to facilitate the growth of less abundant or slow-growing bacteria and thus increased the variety of cultivable bacteria.
Among the cultivable taxa frequently found on brown macroalgal surfaces (such as Laminaria, Saccharina, Fucus, Ascophyllum) are Proteobacteria, Firmicutes, Bacteroidetes, and Actinobacteria, where the latter three phyla are generally less abundant (
The three dominant genera obtained were Limnobacter, Bosea, and Halomonas (Figure 2 and Supplementary Table S3). Limnobacter sp. are oligotrophic freshwater sulfur-oxidizing bacteria (Spring et al., 2001) that occur naturally in aquatic environments (
Members of the genus Bosea are known to be (multi)drug-resistant (
The genus Halomonas comprises cultivable isolates from various saline environments (
In summary, each cultivation strategy resulted in the cultivation of unique strains that were not cultivated with any of the other methods. For example, the application of antibiotics to eliminate Halomonas sp. reduced the competitive pressure between antibiotic resistant bacteria and led to the cultivation of 16 additional bacterial strains. Similar observations have been made in sponges (
The Cultivated vs. Uncultivated Microbiome
Marine pelagic bacteria often have complex growth and nutrient requirements (Stewart, 2012; Zengler, 2013). In addition, they are generally considered to be oligotrophs, since they inhabit a nutrient-poor environment and grow only very slowly, which might also compromise the cultivation process (
Here, we aimed to cultivate bacteria that were associated with the algae/algal cell-walls, a carbohydrate-rich environment due to the accumulation of algal (poly)saccharides, i.e., alginates, fucans, and mannitol (
Our data support this hypothesis since culturability was between 44 and 68% based on the dilution-to-extinction experiments (Table 1). For pelagic studies, culturability is usually below 15%, with some observation going as low as 0.05% (
Culturability was also assessed by comparing the distribution and abundance of taxa obtained in the cultivation study with taxa inferred from16S rRNA gene libraries. In a previous study on Ectocarpus, this type of comparison demonstrated an overall ratio of culturability of 11% based on the presence/absence of OTUs (Tapia et al., 2016). In the present study, this number was further increased with 21% of the OTUs and 47% of all 16S rRNA sequences corresponding to cultivable strains (Figure 3C).
To our knowledge, this is the first study to apply dilution-to-extinction cultivation to macroalgae-associated bacteria, and the standardized cultivation method (
Cultivable Bacteria Not Detected by Metabarcoding
Of the 46 unique strains that were isolated in this study, 16 were isolated at least once from algal tissue grown in NSW, and could thus be directly compared to META2016-NSW metabarcoding data set generated in this study. Seven of them (44%) were represented in this gene library. To be able to compare also strains isolated only from low salinities with metabarcoding data, we included two further data sets obtained for the same strain in 2013. All data sets taken together, 22 of the 46 (48%) strains were found at least in one of the libraries, while 24 were undetectable or below the detection limit. Whether a strain was isolated directly from algal tissue or from the algal culture medium did not have a strong impact on these numbers (Supplementary Table S4).
There are several hypotheses to explain this observation. First, methodological flaws or biases including the inadequacy to extract DNA from certain bacterial cells due to species-specific characteristics (e.g., gram-positive are generally more difficult to extract than gram-negative cells), primers specificity, or PCR conditions (Suzuki and Giovannoni, 1996;
A third explanation is that the sequencing depth or the number of time points examined (one for DNSW two for NSW) may have been too low to identify members of the microbiome that are “rare” (Zilber-Rosenberg and Rosenberg, 2008; Skopina et al., 2016). Bacteria might be present in low abundance in the natural environment but they can amplify rapidly under specific environmental conditions (
Similar observations of cultivable isolates not being detected in corresponding gene libraries have been made in human stool samples (
Perspectives: (Meta)genome-Guided Cultivation and Inference of Metabolic Networks
In this study, we show that a remarkably high number of bacterial cells (∼50%) associated with Ectocarpus was cultivable using a range of cultivation techniques. Each cultivation strategy resulted in another dominant genus or weed-species (Bosea for antibiotic-treated algae, Limnobacter for dilution-to-extinction cultivation) and each strategy also led to the cultivation of unique isolates that were not found with any other cultivation method. Our results thus emphasize the need to use samples from different environmental/abiotic conditions to obtain rare taxa and thus increase the overall cultivable diversity. To further improve these numbers, a metagenomics approach may be used to predict the specific cultivation requirements of yet uncultured taxa (
Regarding the cultivable isolates, genomic data currently in preparation for several strains may be used to predict their metabolic capacities and to generate hypotheses on how they may complement the metabolism of the alga (
The present bacterial culture collection constitutes a valuable tool to study the Ectocarpus holobiont in vitro and complements the genomic tools available for the model Ectocarpus. Together, they can be used to address fundamental questions regarding the functions of brown macroalgal holobionts during exposure to abiotic stressors, for instance during the acclimation to low salinity in E. subulatus.
Statements
Author contributions
All authors conceived the study. HK, CJ, and SD carried out experiments. HK wrote the manuscript with help from SD, CB, and CJ. All authors approved of the final manuscript.
Funding
This work has received funding from the European Union’s Horizon 2020 research and innovation programme under the Marie Sklodowska-Curie grant agreement number 624575 (ALFF) and ANR project IDEALG (ANR-10-BTBR-04) “Investissements d’Avenir, Biotechnologies-Bioressources”.
Acknowledgments
The authors would like to thank Bernard Billoud for help with statistical analyses; Laurence Dartevelle for help with algal culturing; Akira Peters for providing the algal cultures; Dominique Marie for help with the flow cytometry; the Genomer platform (Station Biologique de Roscoff) for access to their sequencing equipment; the ABIMS Platform (Station Biologique de Roscoff) for technical support and server time; Laetitia Mest, Lolita Lecompte, and Maeva Harrivel for their participation in early isolation experiments; Christophe Destombe and Thomas Wichard for helpful discussions; and Angélique Gobet for critical reading of the manuscript.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Supplementary material
The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fmicb.2017.02456/full#supplementary-material
TABLE S1Bacterial growth media recipes for LB, R2A, Zobell, PYG, EC-based, and LNHM.
TABLE S2Antibiotics used to reduce the abundance of Halomonas sp.
TABLE S3Number of bacterial isolates obtained per experimental treatment.
TABLE S4Number of cultivable bacterial strains found in metabarcoding experiments depending on sample origin and sequencing library.
Footnotes
1.^https://blast.ncbi.nlm.nih.gov/Blast.cgi
2.^http://mafft.cbrc.jp/alignment/software
3.^https://www.bioinformatics.babraham.ac.uk/projects/fastqc/
4.^http://hannonlab.cshl.edu/fastx_toolkit/index.html
5.^https://www.mothur.org/wiki/MiSeq_SOP
6.^http://itol.embl.de, version 3.5.3
References
1
AmannR. I.LudwigW.SchleiferK. H. (1995). Phylogenetic identification and in situ detection of individual microbial cells without cultivation.Microbiol. Rev.59143–169.
2
ArahalD.VentosaA. (2006). “The family Halomonadaceae,” inThe Prokaryotes, edsDworkinM.FalkowS.RosenbergE.SchleiferK.-H.StackebrandtE. (New York, NY: Springer), 811–835.
3
BaggesenC.GjermansenC.BrandtA. B. (2014). A Study of Microalgal Symbiotic Communities with the Aim to Increase Biomass and Biodiesel Production.Ph.D. dissertation, DTU Chemical Engineering, Kongens Lyngby.
4
BengtssonM. M.SjøtunK.ØvreåsL. (2010). Seasonal dynamics of bacterial biofilms on the kelp Laminaria hyperborea.Aquat. Microb. Ecol.6071–83. 10.3354/ame01409
5
BoltonJ. J. (1983). Ecoclinal variation in Ectocarpus siliculosus (Phaeophyceae) with respect to temperature growth optima and survival limits.Mar. Biol.73131–138. 10.1007/BF00406880
6
BuergerS.SpoeringA.GavrishE.LeslinC.LingL.EpsteinS. S. (2012). Microbial scout hypothesis, stochastic exit from dormancy, and the nature of slow growers.Appl. Environ. Microbiol.783221–3228. 10.1128/AEM.07307-11
7
BurkeC.ThomasT.LewisM.SteinbergP.KjellebergS. (2011). Composition, uniqueness and variability of the epiphytic bacterial community of the green alga Ulva australis.ISME J.5590–600. 10.1038/ismej.2010.164
8
ButtonD. K.SchutF.QuangP.MartinR.RoberstonB. R. (1993). Viability and isolation of marine bacteria by dilution culture: theory, procedures, and initial results.Appl. Environ. Microbiol.59881–891.
9
CariniP.SteindlerL.BeszteriS.GiovannoniS. J. (2012). Nutrient requirements for growth of the extreme oligotroph “ Candidatus Pelagibacter ubique ” HTCC1062 on a defined medium.ISME J.7592–602. 10.1038/ismej.2012.122
10
ChoJ. C.GiovannoniS. J. (2004). Cultivation and growth characteristics of a diverse group of oligotrophic marine Gammaproteobacteria.Appl. Environ. Microbiol.70432–440. 10.1128/AEM.70.1.432-440.2004
11
CockJ. M.SterckL.RouzéP.ScornetD.AllenA. E.AmoutziasG.et al (2010). The Ectocarpus genome and the independent evolution of multicellularity in brown algae.Nature465617–621. 10.1038/nature09016
12
CoelhoS. M.ScornetD.RousvoalS.PetersN.DartevelleL.PetersA. F.et al (2012). Isolation and regeneration of protoplasts from Ectocarpus.Cold Spring Harb. Protoc.7361–364. 10.1101/pdb.prot067959
13
ConnonS. A.GiovannoniS. J. (2002). High-throughput methods for culturing microorganisms in very-low-nutrient media yield diverse new marine isolates.Appl. Environ. Microbiol.683878–3885. 10.1128/AEM.68.8.3878-3885.2002
14
CroftM. T.LawrenceA. D.Raux-DeeryE.WarrenM. J.SmithA. G. (2005). Algae acquire vitamin B12 through a symbiotic relationship with bacteria.Nature43890–93. 10.1038/nature04056
15
DittamiS. M.Duboscq-BidotL.PerennouM.GobetA.CorreE.BoyenC.et al (2016). Host-microbe interactions as a driver of acclimation to salinity gradients in brown algal cultures.ISME J.1051–63. 10.1038/ismej.2015.104
16
DittamiS. M.EveillardD.TononT. (2014). A metabolic approach to study algal–bacterial interactions in changing environments.Mol. Ecol.231656–1660. 10.1111/mec.12670
17
DittamiS. M.GravotA.GoulitquerS.RousvoalS.PetersA. F.BouchereauA.et al (2012). Towards deciphering dynamic changes and evolutionary mechanisms involved in the adaptation to low salinities in Ectocarpus (brown algae).Plant J.71366–377. 10.1111/j.1365-313X.2012.04982.x
18
DittamiS. M.HeeschS.OlsenJ. L.CollénJ. (2017). Transitions between marine and freshwater environments provide new clues about the origins of multicellular plants and algae.J. Phycol.53731–745. 10.1111/jpy.12547
19
DonachieS. P.FosterJ. S.BrownM. V. (2007). Culture clash: challenging the dogma of microbial diversity.ISME J.197–99. 10.1038/ismej.2007.22
20
DonachieS. P.HouS.LeeK. S.RileyC. W.PikinaA.BelisleC.et al (2004). The hawaiian archipelago: a microbial diversity hotspot.Microb. Ecol.48509–520. 10.1007/s00248-004-0217-1
21
DongS.YangJ.ZhangX. Y.ShiM.SongX. Y.ChenX. L.et al (2012). Cultivable alginate lyase-excreting bacteria associated with the arctic brown alga Laminaria.Mar. Drugs102481–2491. 10.3390/md10112481
22
EdgarR. C.HaasB. J.ClementeJ. C.QuinceC.KnightR. (2011). UCHIME improves sensitivity and speed of chimera detection.Bioinformatics272194–2200. 10.1093/bioinformatics/btr381
23
EganS.HarderT.BurkeC.SteinbergP.KjellebergS.ThomasT. (2013). The seaweed holobiont: understanding seaweed-bacteria interactions.FEMS Microbiol. Rev.37462–476. 10.1111/1574-6976.12011
24
EilersH.PernthalerJ.GlöcknerF.AmannR. (2000). Culturability and in situ abundance of pelagic bacteria from the North Sea.Appl. Environ. Microbiol.663044–3051. 10.1128/AEM.66.7.3044-3051.2000
25
EpsteinS. S. (2009). Microbial awakenings.Nature457:1083. 10.1038/4571083a
26
EstevesA. I. S.AmerN.NguyenM.ThomasT. (2016). Sample processing impacts the viability and cultivability of the sponge microbiome.Front. Microbiol.7:499. 10.3389/fmicb.2016.00499
27
Falcone-DiasM. F.Vaz-MoreiraI.ManaiaC. M. (2012). Bottled mineral water as a potential source of antibiotic resistant bacteria.Water Res.463612–3622. 10.1016/j.watres.2012.04.007
28
Ficko-BleanE.HervéC.MichelG. (2015). Sweet and sour sugars from the sea: the biosynthesis and remodeling of sulfated cell wall polysaccharides from marine macroalgae.Perspect. Phycol.251–64. 10.1127/pip/2015/0028
29
GarzaD. R.DutilhB. E. (2015). From cultured to uncultured genome sequences: metagenomics and modeling microbial ecosystems.Cell. Mol. Life Sci.724287–4308. 10.1007/s00018-015-2004-1
30
GiovannoniS. J.StinglU. (2005). Molecular diversity and ecology of microbial plankton.Nature437343–348. 10.1038/nature04158
31
GoeckeF.LabesA.WieseJ.ImhoffJ. F. (2010). Review chemical interactions between marine macroalgae and bacteria.Mar. Ecol. Prog. Ser.409267–300. 10.3354/meps08607
32
GoeckeF.LabesA.WieseJ.ImhoffJ. F. (2012). Dual effect of macroalgal extracts on growth of bacteria in Western Baltic Sea.Rev. Biol. Mar. Oceanogr.4775–86. 10.4067/S0718-19572012000100007
33
GoeckeF.LabesA.WieseJ.ImhoffJ. F. (2013a). Phylogenetic analysis and antibiotic activity of bacteria isolated from the surface of two co-occurring macroalgae from the Baltic Sea.Eur. J. Phycol.4847–60. 10.1080/09670262.2013.767944
34
GoeckeF.ThielV.WieseJ.LabesA.ImhoffJ. F. (2013b). Algae as an important environment for bacteria - phylogenetic relationships among new bacterial species isolated from algae.Phycologia5214–24. 10.2216/12-24.1.s1
35
GroisillierA.LabourelA.MichelG.TononT. (2015). The mannitol utilization system of the marine bacterium Zobellia galactanovorans.Appl. Environ. Microbiol.811799–1812. 10.1128/AEM.02808-14
36
HollantsJ.LeliaertF.De ClerckO.WillemsA. (2013). What we can learn from sushi: a review on seaweed-bacterial associations.FEMS Microbiol. Ecol.831–16. 10.1111/j.1574-6941.2012.01446.x
37
IvanovaE. P.BakuninaI. Y.SawabeT.HayashiK.AlexeevaY. V.ZhukovaN. V.et al (2002). Two species of culturable bacteria associated with degradation of brown algae Fucus evanescens.Microb. Ecol.43242–249. 10.1007/s00248-001-1011-y
38
Jimenez-InfanteF.NgugiD. K.AlamI.RashidM.BaalawiW.KamauA. A.et al (2014). Genomic differentiation among two strains of the PS1 clade isolated from geographically separated marine habitats.FEMS Microbiol. Ecol.89181–197. 10.1111/1574-6941.12348
39
JoussetA.BienholdC.ChatzinotasA.GallienL.GobetA.KurmV.et al (2017). Where less may be more: how the rare biosphere pulls ecosystems strings.ISME J.11853–862. 10.1038/ismej.2016.174
40
KatohK.MisawaK.KumaK.MiyataT. (2002). MAFFT: a novel method for rapid multiple sequence alignment based on fast Fourier transform.Nucleic Acids Res.303059–3066. 10.1093/nar/gkf436
41
KellerM.ZenglerK. (2004). Tapping into microbial diversity.Nat. Rev. Microbiol.2141–150. 10.1038/nrmicro819
42
Keshtacher-LiebsonE.HadarY.ChenY. (1995). Oligotrophic bacteria enhance algal growth under iron-deficient conditions.Appl. Environ. Microbiol.612439–2441.
43
KongM. K.Kwong-yuC. (1979). A study on the bacterial flora isolated from marine algae.Bot. Mar.2265–82. 10.1515/botm.1979.22.2.83
44
KozichJ. J.WestcottS. L.BaxterN. T.HighlanderS. K.SchlossP. D. (2013). Development of a dual-index sequencing strategy and curation pipeline for analyzing amplicon sequence data on the miseq illumina sequencing platform.Appl. Environ. Microbiol.795112–5120. 10.1128/AEM.01043-13
45
LagierJ. C.ArmougomF.MillionM.HugonP.PagnierI.RobertC.et al (2012). Microbial culturomics: paradigm shift in the human gut microbiome study.Clin. Microbiol. Infect.181185–1193. 10.1111/1469-0691.12023
46
LavyA.KerenR.HaberM.SchwartzI.IlanM. (2014). Implementing sponge physiological and genomic information to enhance the diversity of its culturable associated bacteria.FEMS Microbiol. Ecol.87486–502. 10.1111/1574-6941.12240
47
LetunicI.BorkP. (2016). Interactive tree of life (iTOL) v3: an online tool for the display and annotation of phylogenetic and other trees.Nucleic Acids Res.44W242–W245. 10.1093/nar/gkw290
48
LindhM. V.FigueroaD.SjöstedtJ.BaltarF.LundinD.AnderssonA.et al (2015). Transplant experiments uncover Baltic Sea basin-specific responses in bacterioplankton community composition and metabolic activities.Front. Microbiol.6:223. 10.3389/fmicb.2015.00223
49
LuH.SatoY.FujimuraR.NishizawaT.KamijoT.OhtaH. (2011). Limnobacter litoralis sp. nov., a thiosulfate-oxidizing, heterotrophic bacterium isolated from a volcanic deposit, and emended description of the genus Limnobacter.Int. J. Syst. Evol. Microbiol.61404–407. 10.1099/ijs.0.020206-0
50
MancusoF. P.D’HondtS.WillemsA.AiroldiL.De ClerckO. (2016). Diversity and temporal dynamics of the epiphytic bacterial communities associated with the canopy-forming seaweed Cystoseira compressa (Esper) Gerloff and Nizamuddin.Front. Microbiol.7:476. 10.3389/fmicb.2016.00476
51
MarieD.PartenskyF.JacquetS.VaulotD. (1997). Enumeration and cell cycle analysis of natural populations of marine picoplankton by flow cytometry using the nucleic acid stain SYBR Green I.Appl. Environ. Microbiol.63186–193. 10.1111/j.1365-294X.2009.04480.x
52
MartinM.BarbeyronT.MartinR.PortetelleD.MichelG.VandenbolM. (2015). The cultivable surface microbiota of the brown alga Ascophyllum nodosum is enriched in macroalgal-polysaccharide-degrading bacteria.Front. Microbiol.6:1487. 10.3389/fmicb.2015.01487
53
MichelG.TononT.ScornetD.CockJ. M.KloaregB. (2010). Central and storage carbon metabolism of the brown alga Ectocarpus siliculosus: insights into the origin and evolution of storage carbohydrates in eukaryotes.New Phytol.18867–81. 10.1111/j.1469-8137.2010.03345.x
54
MorrisR. M.RappéM. S.ConnonS. A.VerginK. L.SieboldW. A.CarlsonC. A.et al (2002). SAR11 clade dominates ocean surface bacterioplankton communities.Nature420806–810. 10.1038/nature01240
55
PageK. A.ConnonS. A.GiovannoniS. J. (2004). Representative freshwater bacterioplankton isolated from Crater Lake, Oregon.Appl. Environ. Microbiol.706542–6550. 10.1128/AEM.70.11.6542-6550.2004
56
ParrotD.Antony-BabuS.IntertagliaL.GrubeM.TomasiS.SuzukiM. T. (2015). Littoral lichens as a novel source of potentially bioactive Actinobacteria.Sci. Rep.5:15839. 10.1038/srep15839
57
PedersénM. (1969). Marine brown algae requiring vitamin B12.Physiol. Plant.22977–983. 10.1111/j.1399-3054.1969.tb07455.x
58
PedersénM. (1973). Identification of a Cytokinin, purine, in sea water and the effect of cytokinins on brown algae.Physiol. Plant.28101–105. 10.1111/j.1399-3054.1973.tb01158.x
59
Pedrós-AlióC. (2012). The rare bacterial biosphere.Annu. Rev. Mar. Sci.4449–466. 10.1146/annurev-marine-120710-100948
60
PetersA. F.CoucerioL.TsiamisK.KüpperF. C.ValeroM. (2015). Barcoding of cryptic stages of marine brown algae isolated from incubated substratum reveals high diversity.Cryptogam. Algol.363–29.
61
PetersA. F.MarieD.ScornetD.KloaregB.CockJ. M. (2004). Proposal of Ectocarpus siliculosus (Ectocarpales, Phaeophyceae) as a model organism for brown algal genetics and genomics.J. Phycol.401079–1088. 10.1111/j.1529-8817.2004.04058.x
62
PoliA.KazakH.GürleyendaǧB.TommonaroG.PierettiG.ÖnerE. T.et al (2009). High level synthesis of levan by a novel Halomonas species growing on defined media.Carbohydr. Polym.78651–657. 10.1016/j.carbpol.2009.05.031
63
PopperZ. A.MichelG.HerveC.DomozychD. S.WillatsW. G. T.TuohyM. G.et al (2011). Evolution and diversity of plant cell walls: from algae to flowering plants.Annu. Rev. Plant Biol.62567–590. 10.1146/annurev-arplant-042110-103809
64
QuastC.PruesseE.YilmazP.GerkenJ.SchweerT.YarzaP.et al (2013). The SILVA ribosomal RNA gene database project: improved data processing and web-based tools.Nucleic Acids Res.41D590–D596. 10.1093/nar/gks1219
65
ReasonerD. J.GeldreichE. E. (1985). A new medium for the enumeration and subculture of bacteria from potable water.Appl. Environ. Microbiol.491–7.
66
Rieper-KirchnerM. (1989). Microbial degradation of North Sea macroalgae: field and laboratory studies.Bot. Mar.32241–252. 10.1515/botm.1989.32.3.241
67
RStudio Team (2016). RStudio: Integrated Development for R.Boston, MA: RStudio, Inc.
68
SalaünS.KervarecN.PotinP.HarasD.PiottoM.La BarreS. (2010). Whole-cell spectroscopy is a convenient tool to assist molecular identification of cultivatable marine bacteria and to investigate their adaptive metabolism.Talanta801758–1770. 10.1016/j.talanta.2009.10.020
69
SalaünS.La BarreS.Santos-GoncalvezM.Dos PotinP.HarasD.BazireA. (2012). Influence of exudates of the kelp Laminaria digitata on biofilm formation of associated and exogenous bacterial epiphytes.Microb. Ecol.64359–369. 10.1007/s00248-012-0048-4
70
SawabeT.OhtsukaM.EzuraY. (1997). Novel alginate lyases from marine bacterium Alteromonas sp. strain H-4.Carbohydr. Res.30469–76. 10.1016/S0008-6215(97)00194-8
71
ShadeA.GilbertJ. A. (2015). Temporal patterns of rarity provide a more complete view of microbial diversity.Trends Microbiol.23335–340. 10.1016/j.tim.2015.01.007
72
ShadeA.HoganC. S.KlimowiczA. K.LinskeM.McmanusP. S.HandelsmanJ. (2012). Culturing captures members of the soil rare biosphere.Environ. Microbiol.142247–2252. 10.1111/j.1462-2920.2012.02817.x
73
SinghR. P.ReddyC. R. K. (2014). Seaweed-microbial interactions: key functions of seaweed-associated bacteria.FEMS Microbiol. Ecol.88213–230. 10.1111/1574-6941.12297
74
SinghR. P.ReddyC. R. K. (2016). Unraveling the functions of the macroalgal microbiome.Front. Microbiol.6:1488. 10.3389/fmicb.2015.01488
75
SipkemaD.SchippersK.MaalckeW. J.YangY.SalimS.BlanchH. W. (2011). Multiple approaches to enhance the cultivability of bacteria associated with the marine sponge Haliclona (gellius) sp.Appl. Environ. Microbiol.772130–2140. 10.1128/AEM.01203-10
76
SkopinaM.VasilevaA.PershinaE.PinevichA. (2016). Diversity at low abundance: the phenomenon of the rare bacterial biosphere.Microbiology85272–282. 10.1134/S0026261716030139
77
SoginM. L.MorrisonH. G.HuberJ. A.WelchD. M.HuseS. M.NealP. R.et al (2006). Microbial diversity in the deep sea and the underexplored “rare biosphere”.Proc. Natl. Acad. Sci. U.S.A.10312115–12120. 10.1073/pnas.0605127103
78
SpoernerM.WichardT.BachhuberT.StratmannJ.OertelW. (2012). Growth and thallus morphogenesis of Ulva mutabilis (Chlorophyta) depends on a combination of two bacterial species excreting regulatory factors.J. Phycol.481433–1447. 10.1111/j.1529-8817.2012.01231.x
79
SpringS.KämpferP.SchleiferK. H. (2001). Limnobacter thiooxidans gen. nov., sp. nov., a novel thiosulfate-oxidizing bacterium isolated from freshwater lake sediment.Int. J. Syst. Evol. Microbiol.511463–1470. 10.1099/00207713-51-4-1463
80
StarrR. C.ZeikusJ. A. (1993). Utex – the culture collection of algae at the University of Texas at Austin 1993 List of Cultures.J. Phycol.291–106. 10.1111/j.0022-3646.1993.00001.x
81
StaufenbergerT.ThielV.WieseJ.ImhoffJ. F.JfI.EpI.et al (2008). Phylogenetic analysis of bacteria associated with Laminaria saccharina.FEMS Microbiol. Ecol.6465–77. 10.1111/j.1574-6941.2008.00445.x
82
StewartE. J. (2012). Growing unculturable bacteria.J. Bacteriol.1944151–4160. 10.1128/JB.00345-12
83
StinglU.ChoJ. C.FooW.VerginK. L.LanoilB.GiovannoniS. J. (2008). Dilution-to-extinction culturing of psychrotolerant planktonic bacteria from permanently ice-covered lakes in the McMurdo Dry Valleys, Antarctica.Microb. Ecol.55395–405. 10.1007/s00248-007-9284-4
84
StinglU.TrippH. J.GiovannoniS. J. (2007). Improvements of high-throughput culturing yielded novel SAR11 strains and other abundant marine bacteria from the Oregon coast and the Bermuda Atlantic Time Series study site.ISME J.1361–371. 10.1038/ismej.2007.49
85
SuzukiM. T.GiovannoniS. J. (1996). Bias caused by template annealing in the amplification of mixtures of 16S rRNA genes by PCR.Appl. Environ. Microbiol.62625–630.
86
SuzukiR.ShimodairaH. (2006). Pvclust: an R package for assessing the uncertainty in hierarchical clustering.Bioinformatics221540–1542. 10.1093/bioinformatics/btl117
87
TamuraK.StecherG.PetersonD.FilipskiA.KumarS. (2013). MEGA6: Molecular Evolutionary Genetics Analysis Version 6.0.Mol. Biol. Evol.302725–2729. 10.1093/molbev/mst197
88
TangJ.XiaoY.OshimaA.KawaiH.NagataS. (2008). Disposal of seaweed wakame (Undaria pinnatifida) in composting process by marine bacterium Halomonas sp. AW4.Int. J. Biotechnol.1073–85. 10.1504/IJBT.2008.017970
89
TapiaJ. E.GonzálezB.GoulitquerS.PotinP.CorreaJ. (2016). Microbiota influences morphology and reproduction of the brown alga Ectocarpus sp.Front. Microbiol.7:197. 10.3389/fmicb.2016.00197
90
ThornberC.JonesE.ThomsenM. (2016). “Epibiont-marine macrophyte assemblages,” inMarine Macrophytes As Foundation Species, ed.ÓlafssonE. (New York, NY: CRC Press), 43–65. 10.4324/9781315370781-4
91
TrippH. J.KitnerJ. B.SchwalbachM. S.DaceyJ. W. H.WilhelmL. J.GiovannoniS. J. (2008). SAR11 marine bacteria require exogenous reduced sulphur for growth.Nature452741–744. 10.1038/nature06776
92
TroussellierM.EscalasA.BouvierT.MouillotD. (2017). Sustaining rare marine microorganisms: macroorganisms as repositories and dispersal agents of microbial diversity.Front. Microbiol.8:947. 10.3389/fmicb.2017.00947
93
Vaz-MoreiraI.EgasC.NunesO. C.ManaiaC. M. (2013). Bacterial diversity from the source to the tap: a comparative study based on 16S rRNA gene-DGGE and culture-dependent methods.FEMS Microbiol. Ecol.83361–374. 10.1111/1574-6941.12002
94
WahlM.GoeckeF.LabesA.DobretsovS.WeinbergerF. (2012). The second skin: ecological role of epibiotic biofilms on marine organisms.Front. Microbiol.3:292. 10.3389/fmicb.2012.00292
95
WangG.ShuaiL.LiY.LinW.ZhaoX.DuanD. (2008). Phylogenetic analysis of epiphytic marine bacteria on Hole-Rotten diseased sporophytes of Laminaria japonica.J. Appl. Phycol.20403–409. 10.1007/s10811-007-9274-4
96
WangQ.GarrityG. M.TiedjeJ. M.ColeJ. R. (2007). Naïve Bayesian classifier for rapid assignment of rRNA sequences into the new bacterial taxonomy.Appl. Environ. Microbiol.735261–5267. 10.1128/AEM.00062-07
97
WeisburgW. G.BarnsS. M.PelletierD. A.LaneD. J. (1991). 16S ribosomal DNA amplification for phylogenetic study.J. Bacteriol.173697–703. 10.1128/jb.173.2.697-703
98
WellsM. L.PotinP.CraigieJ. S.RavenJ. A.MerchantS. S.HelliwellK. E.et al (2017). Algae as nutritional and functional food sources: revisiting our understanding.J. Appl. Phycol.29949–982. 10.1007/s10811-016-0974-5
99
WestJ.KraftG. (1996). Ectocarpus siliculosus (Dillwyn) Lyngb. from Hopkins River Falls, Victoria – the first record of a freshwater brown alga in Australia.Muelleria929–33.
100
WieseJ.ThielV.NagelK.StaufenbergerT.ImhoffJ. F. (2009). Diversity of antibiotic-active bacteria associated with the brown alga Laminaria saccharina from the baltic sea.Mar. Biotechnol.11287–300. 10.1007/s10126-008-9143-4
101
WongT. Y.PrestonL. A.SchillerN. L. (2000). Alginate lyase: review of major sources and enzyme characteristics, structure-function analysis, biological roles, and applications.Annu. Rev. Microbiol.54289–340. 10.1146/annurev.micro.54.1.289
102
WuH. T.MiZ. L.ZhangJ. X.ChenC.XieS. G. (2014). Bacterial communities associated with an occurrence of colored water in an urban drinking water distribution system.Biomed. Environ. Sci.27646–650. 10.3967/bes2014.099
103
YangS.-J.KangI.ChoJ.-C. (2016). Expansion of cultured bacterial diversity by large-scale dilution-to-extinction culturing from a single seawater sample.Microb. Ecol.7129–43. 10.1007/s00248-015-0695-3
104
ZenglerK. (2013). “To grow or not to grow: isolation and cultivation procedures in the genomic age,” in The Human Microbiota, ed.FredricksD. N. (Hoboken, NJ: John Wiley & Sons, Inc.), 289–302. 10.1002/9781118409855.ch12
105
ZhangL.GaoG.TangX.ShaoK. (2014). Impacts of different salinities on bacterial biofilm communities in fresh water.Can. J. Microbiol.60319–326. 10.1139/cjm-2013-0808
106
Zilber-RosenbergI.RosenbergE. (2008). Role of microorganisms in the evolution of animals and plants: the hologenome theory of evolution.FEMS Microbiol. Rev.32723–735. 10.1111/j.1574-6976.2008.00123.x
107
ZobellC. (1941). Cultural requirements of marine heterotrophic aerobes.J. Mar. Res.442–75.
108
ZothanpuiaPassariA. K.GuptaV. K.SinghB. P. (2016). Detection of antibiotic-resistant bacteria endowed with antimicrobial activity from a freshwater lake and their phylogenetic affiliation.PeerJ4:e2103. 10.7717/peerj.2103
Summary
Keywords
Ectocarpus, holobiont, bacterial cultivation, brown macroalgae, dilution-to-extinction, metabarcoding
Citation
KleinJan H, Jeanthon C, Boyen C and Dittami SM (2017) Exploring the Cultivable Ectocarpus Microbiome. Front. Microbiol. 8:2456. doi: 10.3389/fmicb.2017.02456
Received
19 September 2017
Accepted
27 November 2017
Published
11 December 2017
Volume
8 - 2017
Edited by
Tilmann Harder, University of Bremen, Germany
Reviewed by
Meinhard Simon, University of Oldenburg, Germany; Suhelen Egan, University of New South Wales, Australia
Updates

Check for updates
Copyright
© 2017 KleinJan, Jeanthon, Boyen and Dittami.
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) or licensor are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Hetty KleinJan, hetty.kleinjan@sb-roscoff.fr; hettykleinjan@gmail.com Simon M. Dittami, simon.dittami@sb-rocoff.fr; simon.dittami@gmail.com
This article was submitted to Microbial Symbioses, a section of the journal Frontiers in Microbiology
Disclaimer
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.