Abstract
The phylogenetic diversity of microorganisms in marine sponges is becoming increasingly well described, yet relatively little is known about the activities of these symbionts. Given the seemingly favourable environment provided to microbes by their sponge hosts, as indicated by the extraordinarily high abundance of sponge symbionts, we hypothesized that the majority of sponge-associated bacteria are active in situ. To test this hypothesis we compared, for the first time in sponges, 16S rRNA gene- vs 16S rRNA-derived bacterial community profiles to gain insights into symbiont composition and activity, respectively. Clone libraries revealed a highly diverse bacterial community in Ancorina alata, and a much lower diversity in Polymastia sp., which were identified by electron microscopy as a high- and a low-microbial abundance sponge, respectively. Substantial overlap between DNA and RNA libraries was evident at both phylum and phylotype levels, indicating in situ activity for a large fraction of sponge-associated bacteria. This active fraction included uncultivated, sponge-specific lineages within, for example, Actinobacteria, Chloroflexi and Gemmatimonadetes. This study shows the potential of RNA vs DNA comparisons based on the 16S rRNA gene to provide insights into the activity of sponge-associated microorganisms.
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Introduction
Many marine sponges harbour dense and diverse microbial communities of considerable ecological and biotechnological importance (Hentschel et al., 2006; Taylor et al., 2007b). These communities, which can include bacteria, archaea and eukaryotic microorganisms, are often quite specific to sponges, with many microbial phylotypes appearing to live exclusively within sponge hosts and not in the surrounding seawater (Hentschel et al., 2002; Taylor et al., 2007b; Schmitt et al., 2008). Although our understanding of the microbial diversity in sponges is rapidly improving, much remains unknown about the activity of these microbes (Taylor et al., 2007a). Specific microbially mediated processes within sponges, such as photosynthesis, sulphate reduction, nitrogen fixation and nitrification, have been quantified and in many cases the relevant microbes have been identified (Wilkinson and Fay, 1979; Wilkinson, 1983; Diaz and Ward, 1997; Wilkinson et al., 1999; Hoffmann et al., 2005, 2009; Hallam et al., 2006; Bayer et al., 2008; Mohamed et al., 2008a, 2009; Steger et al., 2008). These studies, which have utilized methods such as isotope enrichments, metagenomics and functional gene analyses, have extended our knowledge of symbiont function in sponges, yet they remain focused on specific processes or particular functional groups of organisms. What is lacking to date is a community-wide assessment of microbial activity in marine sponges. This would be useful, as identification of those sponge-associated microbes that are active in situ is an important step towards elucidating their ecological role and contribution to the host.
All living organisms contain ribosomal RNA, and these molecules have become the gold standard for microbial ecology and taxonomy (Ludwig and Schleifer, 1999; Tringe and Hugenholtz, 2008). The analysis of 16S rRNA genes through clone libraries and fingerprinting approaches such as denaturing gradient gel electrophoresis (DGGE) has greatly extended our knowledge about the phylogenetic richness of sponge-associated bacteria and archaea (Webster et al., 2001, 2004; Hentschel et al., 2002; Taylor et al., 2004, 2007b; Holmes and Blanch, 2006; Longford et al., 2007; Schmitt et al., 2007, 2008; Thiel et al., 2007; Mohamed et al., 2008b; Zhu et al., 2008). Researchers in other systems have taken this approach one step further, yielding insights into both richness and activity by comparing 16S rRNA gene- and 16S rRNA-derived sequences, respectively (Moeseneder et al., 2001, 2005; Winter et al., 2001; Troussellier et al., 2002; Mills et al., 2005; Gentile et al., 2006; Martinez et al., 2006; Brinkmann et al., 2008; McIlroy et al., 2008; West et al., 2008; Rodriguez-Blanco et al., 2009). In general, cellular concentrations of rRNA are correlated with growth rate and activity (DeLong et al., 1989; Poulsen et al., 1993), hence—with acknowledgement of certain caveats (e.g., for ammonia-oxidizing bacteria; Morgenroth et al., 2000)—the rRNA itself can yield useful information about which community members are active.
In this study we investigated bacterial community composition (16S rRNA gene) and activity (16S rRNA) in two marine sponges from northeastern New Zealand. Clone libraries, generating a total of 313 sequences, were constructed from the high-microbial-abundance sponge Ancorina alata (Demospongiae: Astrophorida: Ancorinidae) and the low-microbial-abundance sponge Polymastia sp. (Demospongiae: Hadromerida: Polymastiidae). The existence of both high- and low-microbial-abundance sponges is well documented (Vacelet and Donadey, 1977; Reiswig, 1981; Hentschel et al., 2006; Weisz et al., 2008), although the exact reasons for these differences in microbial loads are uncertain. In addition to the well-characterized taxa, such as the Alpha- and Gammaproteobacteria, activity was inferred for uncultivated, sponge-specific lineages within phyla, including the Gemmatimonadetes, Chloroflexi and a taxon of uncertain affiliation related to the sponge-specific ‘Poribacteria’ (Fieseler et al., 2004). Moreover, our results show the potential of rRNA gene vs rRNA comparisons to provide insights into the activity of sponge-associated microorganisms.
Materials and methods
Sponge sampling
Small samples were taken from three individuals of each of the sponges A. alata and Polymastia sp. (both class Demospongiae). Sampling was carried out by SCUBA diving at depths of 3–10 m at Mathesons Bay (36°18′S, 174°47′E) and Jones Bay (36°23′S, 174°49′E), northeastern New Zealand, in November/December 2008. Tissue samples were transferred into RNAlater (Applied Biosystems/Ambion, Foster City, CA, USA), then transported to the laboratory on ice before freezing at −80 °C. Samples were subsequently freeze-dried and stored again at −80 °C. Tissue samples for electron microscopy were cut into small pieces of about 1 mm3, fixed in 2.5% glutaraldehyde double-distilled water, and kept overnight at 4 °C before processing.
Transmission electron microscopy (TEM)
Fixed sponge samples (three individuals per sponge) were washed five times in cacodylate buffer (50 mM, pH 7.2), fixed in 2% osmium tetroxide for 90 min, washed five times in double-distilled water, and incubated overnight in 0.5% uranyl acetate. After dehydration in an ethanol series (30%, 50%, 70%, 90%, 96%, and three times at 100% for 30 min each), samples were incubated three times for 30 min in 1 × propylene oxide, maintained overnight in 1:1 (vol/vol) propylene oxide-Epon 812 (EM bed-812, Electron Microscopy Science, Hatfield, PA, USA), incubated twice for 2 h in Epon 812, and finally embedded in Epon 812 for 48 h at 60 °C. Samples were then sectioned with an ultramicrotome (Leica, Wetzlar, Germany; EM UC6) and examined by TEM (Philips CM12, Fei Company, Hillsboro, OR, USA).
Nucleic acid extraction and construction of 16S rRNA gene/rRNA clone libraries
Total DNA and RNA were co-extracted from 5–6 mg of freeze-dried sponge tissue using the AllPrep DNA/RNA mini kit (Qiagen, Hilden, Germany). Extractions were performed separately for all three individuals of both species (A. alata and Polymastia sp.). The RNA extract was subsequently purified by DNA digestion for 60 min using RQ1 RNase-free DNase (Promega, Madison, WI, USA) and RNA was reverse-transcribed into cDNA using random hexamers in the SuperScript III First Strand Synthesis System (Invitrogen, Carlsbad, CA, USA). Afterwards, DNA, cDNA and RNA were PCR-amplified with the universal bacterial primers 616V (5′-AGAGTTTGATYMTGGCTC-3′) and 1492R (5′-GGYTACCTTGTTACGACTT-3′) (Kane et al., 1993; Juretschko et al., 1998), spanning a ∼1500 bp region of the 16S rRNA gene. The RNA template served as a control in the PCR and did not give any products. Cycling conditions on a T1 Thermocycler (Biometra, Goettingen, Germany) were as follows: initial denaturing step at 95 °C for 5 min, 30 cycles of denaturing at 95 °C for 1 min, primer annealing at 54 °C for 1 min and elongation at 72 °C for 90 s, followed by a final extension step at 72 °C for 10 min. The PCR products from each sponge species representing the respective DNA and cDNA fractions were pooled and ligated into the pGEM-T-easy vector (Promega) and clone libraries were constructed according to the manufacturer's instructions (four libraries in total). Pooling of PCR products was justified given that corresponding denaturing gradient gel electrophoresis profiles based on DNA and RNA revealed high inter-individual similarities (data not shown). Clones that contained an insert (as evaluated by blue/white colony screening) were grown overnight at 37 °C. After a lysis step for 30 min at 94 °C, a PCR was performed with the vector-specific primers PGEM-F and PGEM-R (Aislabie et al., 2009), to determine which clones contained a correct-sized insert. Cycling conditions were the same as described above. In total, 375 (192 for Polymastia sp. and 183 for A. alata) PCR products were sequenced by Macrogen (Seoul, Korea), and, after the removal of poor quality sequences and chimeric sequences (n=62) detected with Pintail (Ashelford et al., 2005), the final sequence data (81 near-full length (>1200 bp) and 232 partial sequences) were submitted to the DDBJ/EMBL/GenBank databases under accession numbers FJ900272–FJ900584.
Statistical and phylogenetic analyses
The nonparametric richness estimator Chao1, used to evaluate how much of the richness in each library was sequenced, was calculated at different operational taxonomic unit (OTU) thresholds using DOTUR implented in Mothur (Schloss and Handelsman, 2005). Preliminary phylogenetic affiliations were obtained for all DNA- and cDNA (RNA)-derived sequences using the NCBI's BLAST server (http://blast.ncbi.nlm.nih.gov/Blast.cgi). Sequences from A. alata and Polymastia sp., as well as their closest relatives identified by BLAST, were aligned using the web-based SINA aligner, then imported into a 16S rRNA ARB-SILVA database (Ludwig et al., 2004; Pruesse et al., 2007) (version 96, containing 271 543 bacterial rRNA sequences) for subsequent manual refinement of the alignment (inspection of the automatic alignment by eye and manual corrections where appropriate using the editor tool in the ARB software package). Maximum likelihood, maximum parsimony and neighbor-joining trees were calculated in ARB using long (⩾1200 bp) sequences only. Shorter sequences were added using the parsimony interactive tool in ARB without altering the tree topology. Phylogenetic consensus trees, using the maximum likelihood tree as a backbone, were manually constructed (Ludwig et al., 1998). Maximum parsimony bootstraps (1000 resamplings) were performed to further assess the stability of observed branching patterns.
Results
Examination of sponge mesohyl (three individuals per species) by TEM revealed the presence of large numbers of extracellular, morphologically diverse microorganisms within the sponge A. alata, whereas very few microbial cells were seen in Polymastia sp. (Figure 1). We thus deem A. alata to be a ‘high-microbial-abundance’ sponge (sensu; Hentschel et al., 2006), whereas Polymastia sp. is a ‘low-microbial-abundance’ sponge.
A total of 313 sequences was obtained from the sponges A. alata and Polymastia sp., all of which were of bacterial origin. Of the 157 sequences from A. alata, 78 were derived from the 16S rRNA gene and 79 from 16S rRNA. For Polymastia sp. we obtained 85 16S rRNA gene sequences and 71 sequences from 16S rRNA. Bacterial phylum-level richness was much higher in the A. alata libraries, with members of eight phyla (including three Proteobacteria classes) recovered from the DNA fraction, and seven of these also occurring in the RNA fraction (Figures 2, 3, 4 and 5, Supplementary Figures 1–4). When a 99% sequence similarity threshold was used to define an OTU, 43 OTUs were found in the A. alata DNA-derived library, whereas 31 OTUs were found when a 95% OTU definition was applied. The Chao1 estimates of total OTU richness were 73 and 35 for the 99% and 95% OTUs, respectively. In the A. alata RNA library, thirty-eight 99% OTUs were identified (Chao1 estimate=74), whereas thirty 95% OTUs were found (Chao1=45). The Polymastia sp. DNA library comprised only two bacterial phyla, with three represented in the RNA library (Figures 2, 3, 4 and 5, Supplementary Figures 1–4). Fourty-five 99% OTUs were found in the DNA library (Chao1=279), with twenty-two 95% OTUs recovered (Chao1=37). In the RNA library from Polymastia sp., sixteen 99% OTUs were found (Chao1=21), compared with thirteen 95% OTUs (Chao1=15).
At the phylum level, the compositions of the DNA- and RNA-derived libraries from A. alata were very similar (Figure 2). The most abundant taxa in both libraries were the class Gammaproteobacteria (21% of DNA clones and 34% of RNA clones) and the Chloroflexi-affiliated organisms (32% of DNA clones and 20% of RNA clones). Other taxa represented in both libraries were the Acidobacteria, Actinobacteria, Bacteroidetes, Gemmatimonadetes, Alpha- and Deltaproteobacteria, and a lineage of uncertain affiliation that seems to fall within the Planctomycetes–Verrucomicrobia–Chlamydiae (PVC) superphylum (Wagner and Horn, 2006). The only major taxon to be recovered from only one library was the Nitrospirae, for which a single sequence was found in the DNA-derived library. Phylogenetic consensus trees were constructed for all obtained sequences, and examination of these reveals the extent of overlap between DNA and RNA libraries at the phylotype level as indicated by clusters A1–A16 in Figures 3, 4 and 5 and Supplementary Figures 1–4. For example, concordance between the libraries was high within the Actinobacteria (Figure 3), in which both DNA and RNA clones (cluster A1) occurred within a sponge-specific cluster. In addition, there was an RNA phylotype without a corresponding DNA sequence, and DNA phylotypes with no matching RNA sequences. Similar results were evident for the other bacterial phyla (Figures 4 and 5, Supplementary Figures 1–4), in which there were typically some overlapping DNA and RNA sequences but also examples of DNA or RNA sequences on their own.
The Polymastia sp. clone libraries were much less diverse than those of A. alata (Figure 2). The DNA library was dominated (84% of clones) by a single Alphaproteobacteria lineage (Supplementary Figure 2), with the remaining sequences falling elsewhere within the Alphaproteobacteria and within one Actinobacteria lineage (Figure 3). Both the Alphaproteobacteria (cluster P2; Supplementary Figure 2) and Actinobacteria (cluster P1; Figure 3) were also represented in the RNA-derived library, although the Alphaproteobacteria comprised only 24% of the sequenced clones. Although absent from the DNA library, the Gammaproteobacteria were well represented in the RNA library, with several phylotypes together making up 45% of the recovered clones (Supplementary Figure 1). Spirochaetes were also abundant in the RNA library, comprising 18% of clones (Supplementary Figure 4), but were absent from the DNA library.
Consistent with previous studies, many of the sequences obtained in this study fell into monophyletic, sponge-specific sequence clusters (Hentschel et al., 2002). These occurred to varying extents in all recovered bacterial phyla, although some clusters within the Chloroflexi (Figure 4), Gemmatimonadetes (Figure 5), Nitrospirae and Deltaproteobacteria (both Supplementary Figure 4) also contained at least one coral-derived sequence.
Discussion
This study represents the first community-wide approach to investigating bacterial activity in marine sponges. Previous studies have provided valuable information on specific metabolic processes and/or the organisms involved, but to gain a broader picture of microbial diversity and activity within any system it is essential to consider the whole community. By comparing 16S rRNA gene and 16S rRNA profiles of bacterial identity and activity, respectively, we were able to provide insights into the in situ activity of uncultivated, sponge-specific bacterial lineages. Taxa such as the Actinobacteria, Chloroflexi, Gemmatimonadetes and Acidobacteria contain large sponge-specific clusters from diverse host sponges; yet, a failure to obtain most of these organisms in pure culture has led to a paucity of information about their activities and likely function within the host.
Bacterial 16S rRNA gene vs 16S rRNA comparisons in sponges
Earlier studies have successfully used the 16S rRNA gene vs rRNA approach to investigate the activity of, for example, marine plankton, sediment and gas hydrate communities (Moeseneder et al., 2001, 2005; Mills et al., 2005; Gentile et al., 2006; Rodriguez-Blanco et al., 2009). Similar to earlier studies, we found substantial overlap between the DNA- and RNA-derived libraries (clusters A1–16 and P1 and 2 in Figures 3, 4 and 5, and Supplementary Figures 1–4), but also many cases in which a particular DNA or RNA sequence occurred alone (e.g., both phenomena can be seen for the Actinobacteria in Figure 3). Each of these cases can be readily explained—or at least speculated upon (Moeseneder et al., 2005). First, phylotypes from the same sponge species represented in both DNA and RNA libraries are clearly present and—as indicated by the detection of their rRNA—are presumably active as well. This is the case for, for example, cluster A1 in Figure 3. On this same tree, the A. alata DNA clones AncD11, AncA12, AncD8 and AncE1 may represent abundant bacteria and/or those that contain multiple 16S rRNA gene operons. The absence of matching clones in the RNA library implies that the bacteria represented by these sequences may have only low activity. RNA clones without corresponding DNA clones (e.g., AncK22, AncL22 and AncL39 in Figure 3) may represent bacteria that are uncommon but metabolically highly active. It is worth noting here that a conservative approach was taken, with any inferences about bacterial activity remaining strictly qualitative.
Discrepancies between DNA- and RNA-derived libraries can often be explained within a biological context, as discussed above. However, it is also worthwhile to consider methodological factors that could potentially contribute to such variation among libraries. Most critically, the entire approach is based on the use of rRNA as a proxy for activity. Although it is now known that ammonia-oxidizing bacteria retain appreciable cellular concentrations of rRNA even during idle periods when activity is expected to be minimal (Morgenroth et al., 2000), it is widely accepted that in most bacteria rRNA levels are typically correlated with cellular growth rate and activity (DeLong et al., 1989; Poulsen et al., 1993). The approach therefore seems valid for most bacteria in most situations, although further investigation of host-associated microbes is required to establish definitively the relationship between rRNA level and activity for symbionts. In addition, small cells are likely to have a lower ribosomal RNA content when compared with larger cells, even though they could be metabolically more active. Another point to consider is that a specific sequence could be detected in one (i.e., either DNA or RNA) library but missed in the corresponding library because of insufficient numbers of clones being sequenced. Thus, a difference between DNA and RNA libraries would seem to be present, when in fact there is none. Given the considerable overlap between our DNA- and RNA-derived libraries, we do not believe this to be a major factor in our case, although this does depend on the phylotype definition used. If an exclusively monophyletic grouping of DNA- or RNA-derived sequences is used to define a phylotype, then concordance between the libraries is high. However, one can also consider the case in which phylotypes are defined based on a—somewhat arbitrary—sequence similarity threshold (e.g., 99% may represent ‘species’, whereas 95% may approximate ‘genus’ level). Using a 95% threshold, observed OTU richness was almost as high in the A. alata DNA library as the total richness predicted by the Chao1 estimator, suggesting that further sequencing of this library would have revealed very few additional genera. Predictably, the observed and predicted OTU richness values diverge more when a more stringent (99%) OTU threshold is used. Similar results can be seen for other libraries, indicating that further sequencing could potentially eliminate some of the observed differences between DNA- and RNA-derived libraries. Irrespective of this, the overall conclusion, that a large fraction of sponge-associated bacteria are active in situ, is not affected. What is worth noting is the seemingly low coverage of the DNA-derived library from Polymastia sp. The observed number of 99% OTUs in this library was 45, whereas an OTU richness of 279 was estimated by the Chao1 analysis. Interestingly, only twenty-two 95%-OTUs were found, whereas the corresponding Chao1 estimate fell to only 37. The vast majority of sequences in this library fall into one monophyletic cluster within the Alphaproteobacteria, with a minimum pairwise similarity of 93.7%; thus, there is evidently a high level of microdiversity (‘species-level’) in this cluster, but almost all sequences belong to the same ‘genus’ (95%).
We used clone libraries to provide the highest degree of phylogenetic information (through the generation of full-length 16S sequences) while demonstrating the effectiveness of the combined DNA vs RNA approach for sponges. However, other techniques are more appropriate in situations requiring high sample numbers, for example when examining biological and/or environmental variability. Fortunately, the DNA vs RNA approach is equally applicable to high-throughput community fingerprinting techniques such as denaturing gradient gel electrophoresis (Winter et al., 2001; Troussellier et al., 2002), terminal restriction fragment length polymorphism (T-RFLP) (Moeseneder et al., 2001) and single-stranded conformational polymorphism (SSCP) (West et al., 2008; Rodriguez-Blanco et al., 2009). It could also be used in conjunction with next-generation sequencing methods such as tag pyrosequencing (Sogin et al., 2006; Huse et al., 2008). Our laboratory is currently investigating this for sponges, with the aim of detecting bacterial activity in both rare and abundant community members.
New insights into the in situ activity of sponge-associated bacteria
Marine sponges fall into one of two main categories with respect to their associated microorganisms. High-microbial-abundance sponges contain very dense communities of diverse microorganisms. In these sponges, microbes occur at densities of up to 1010 cells per gram wet weight of sponge and their collective biomass may rival that of the host sponge cells (Vacelet, 1975; Friedrich et al., 2001). Our TEM data indicate that the New Zealand sponge A. alata belongs to this category (Figure 1A). Our second sponge, Polymastia sp., exhibited much lower densities of microbes in the mesohyl (Figure 1B) and therefore seems typical of a low-microbial-abundance sponge, which tend to have microbial densities of 105–106 cells per gram, similar to that of seawater (Hentschel et al., 2006). In addition, A. alata and Polymastia sp. also differ in the fact that the latter sponge has a much lower bacterial sequence richness, with only three phyla detected compared with eight in A. alata (Figure 2).
Within each sponge, the DNA and RNA libraries showed considerable overlap, indicating that a substantial fraction of the bacterial community within both sponges was physiologically active. This is evident at the levels of both phylum and specific sequence types, with overlapping phylotypes marked by boxes in Figures 3, 4 and 5 and Supplementary Figures 1–4. In Polymastia sp., corresponding DNA and RNA phylotypes were found in two major clusters, one within the Actinobacteria (P1, Figure 3) and the other within the Alphaproteobacteria (P2, Supplementary Figure 2). Interestingly, about one-third of all RNA clones, and almost all DNA clones, fell within these two clusters. Phylotypes P1 and P2 might therefore represent true symbionts of Polymastia sp., although this needs to be confirmed by future studies. In contrast, many remaining RNA clones, mainly within Gammaproteobacteria and Spirochaetes, could represent highly active bacteria serving as food or being contaminants from seawater. Many of these clones cluster with sequences from non-sponge sources (Figures 3, 4 and 5, Supplementary Figures 1–4). In A. alata, corresponding DNA and RNA phylotypes were distributed among seven different phyla, thus encompassing almost the entire bacterial diversity found in this sponge. Activity was therefore not restricted to a specific phylogenetic group of bacteria, but rather to a phylogenetically complex bacterial community.
Many of the detected phylotypes in A. alata (including those found at both DNA and RNA levels) were similar to sequences derived from other sponges, or even fell within monophyletic sponge-specific clusters. Much recent attention has been focused on the phenomenon that even distantly related sponges from different oceans share a subset of their microbial communities that is not found outside sponge hosts (Hentschel et al., 2002; Taylor et al., 2007b). This is particularly the case for the high-microbial-abundance sponges, which contain numerous lineages that are apparently absent from other environments. However, despite this interest, there is still little known about the nature of these symbioses. The function of sponge-specific microbes has only been determined for certain microbial groups that are responsible for, for example, photosynthesis, nitrification or sulphate reduction in sponges (Wilkinson, 1983; Hoffmann et al., 2005; Bayer et al., 2008). This study suggests that in fact many of the sponge-specific symbionts are active within their respective host sponges.
The activity patterns described here for microbial consortia in A. alata and Polymastia sp. represent only a snapshot at a single time point. Microbial activities may be heavily influenced by host biology and other environmental factors. For example, the pumping activity of a sponge influences the oxygenation of its mesohyl matrix (Hoffmann et al., 2008). The mesohyl of the Mediterranean sponge Aplysina aerophoba was well oxygenated while the sponge was pumping water through its body, but became anoxic minutes after pumping ceased (Hoffmann et al., 2008). It is easily conceivable that in the first circumstance aerobic microbes are active, whereas under anoxic conditions anaerobic microbes would be more active. Additional, chemical and physical factors that might influence the activity of sponge-associated microbes include changes in temperature, salinity, light or turbulence. The combined 16S rRNA and 16S rRNA gene approach offers a way to evaluate activity changes within the overall sponge microbial community, whereas analyses of mRNA could give more insights into which specific pathways are being affected.
Concluding remarks
In this study we have successfully shown the application of the 16S rRNA gene vs rRNA approach to marine sponge-associated bacteria. In the process, we were able to provide the first insights into the in situ activity of uncultivated, sponge-specific bacterial lineages. There is a compelling argument for including both rRNA gene and rRNA analyses in future investigations of sponge-associated microorganisms, as the combined approach allows identification of phylotypes that would remain hidden when DNA or RNA clones are examined in isolation. Furthermore, it helps us to tackle one of the key focal points for sponge microbiology research (Taylor et al., 2007a), the challenge of elucidating symbiont activity and function.
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References
Aislabie J, Jordan S, Ayton J, Klassen JL, Barker GM, Turner S . (2009). Bacterial diversity associated with ornithogenic soil of the Ross Sea region, Antarctica. Can J Microbiol 55: 21–36.
Ashelford KE, Chuzhanova NA, Fry JC, Jones AJ, Weightman AJ . (2005). At least 1 in 20 16S rRNA sequence records currently held in public repositories is estimated to contain substantial anomalies. Appl Environ Microbiol 71: 7724–7736.
Bayer K, Schmitt S, Hentschel U . (2008). Physiology, phylogeny and in situ evidence for bacterial and archaeal nitrifiers in the marine sponge Aplysina aerophoba. Environ Microbiol 10: 2942–2955.
Brinkmann N, Martens R, Tebbe CC . (2008). Origin and diversity of metabolically active gut bacteria from laboratory-bred larvae of Manduca sexta (Sphingidae, Lepidoptera, Insecta). Appl Environ Microbiol 74: 7189–7196.
DeLong EF, Wickham GS, Pace NR . (1989). Phylogenetic stains: ribosomal RNA-based probes for the identification of single cells. Science 243: 1360–1363.
Diaz MC, Ward BB . (1997). Sponge-mediated nitrification in tropical benthic communities. Mar Ecol Prog Ser 156: 97–107.
Fieseler L, Horn M, Wagner M, Hentschel U . (2004). Discovery of the novel candidate phylum ‘Poribacteria’ in marine sponges. Appl Environ Microbiol 70: 3724–3732.
Friedrich AB, Fischer I, Proksch P, Hacker J, Hentschel U . (2001). Temporal variation of the microbial community associated with the Mediterranean sponge Aplysina aerophoba. FEMS Microbiol Ecol 38: 105–113.
Gentile G, Giuliano L, D′Auria G, Smedile F, Azzaro M, De Domenico M et al. (2006). Study of bacterial communities in Antarctic coastal waters by a combination of 16S rRNA and 16S rDNA sequencing. Environ Microbiol 8: 2150–2161.
Hallam SJ, Mincer TJ, Schleper C, Preston CM, Roberts K, Richardson PM et al. (2006). Pathways of carbon assimilation and ammonia oxidation suggested by environmental genomic analyses of marine Crenarchaeota. PLoS Biol 4: e95.
Hentschel U, Usher KM, Taylor MW . (2006). Marine sponges as microbial fermenters. FEMS Microbiol Ecol 55: 167–177.
Hentschel U, Hopke J, Horn M, Friedrich AB, Wagner M, Hacker J et al. (2002). Molecular evidence for a uniform microbial community in sponges from different oceans. Appl Environ Microbiol 68: 4431–4440.
Hoffmann F, Larsen O, Thiel V, Rapp HT, Pape T, Michaelis W et al. (2005). An anaerobic world in sponges. Geomicrobiol J 22: 1–10.
Hoffmann F, Radax R, Woebken D, Holtappels M, Lavik G, Rapp HT et al. (2009). Complex nitrogen cycling in the sponge Geodia barretti. Environ Microbiol 11: 2228–2243.
Hoffmann F, Roy H, Bayer K, Hentschel U, Pfannkuchen M, Brummer F et al. (2008). Oxygen dynamics and transport in the Mediterranean sponge Aplysina aerophoba. Mar Biol 153: 1257–1264.
Holmes B, Blanch H . (2006). Genus-specific associations of marine sponges with group I crenarchaeotes. Mar Biol 150: 759–772.
Huse SM, Dethlefsen L, Huber JA, Welch DM, Relman DA, Sogin ML . (2008). Exploring microbial diversity and taxonomy using SSU rRNA hypervariable tag sequencing. PLoS Genet 4: e1000255.
Juretschko S, Timmermann G, Schmid M, Schleifer KH, Pommerening-Roser A, Koops HP et al. (1998). Combined molecular and conventional analyses of nitrifying bacterium diversity in activated sludge: Nitrosococcus mobilis and Nitrospira like bacteria as dominant populations. Appl Environ Microbiol 64: 3042–3051.
Kane MD, Poulsen LK, Stahl DA . (1993). Monitoring the enrichment and isolation of sulfate-reducing bacteria by using oligonucleotide hybridization probes designed from environmentally derived 16S rRNA sequences. Appl Environ Microbiol 59: 682–686.
Longford SR, Tujula NA, Crocetti GR, Holmes AJ, Holmström C, Kjelleberg S et al. (2007). Comparisons of diversity of bacterial communities associated with three sessile marine eukaryotes. Aquat Microb Ecol 48: 217–229.
Ludwig W, Schleifer K-H . (1999). Phylogeny of Bacteria beyond the 16S rRNA standard. ASM News 65: 752–757.
Ludwig W, Strunk O, Klugbauer S, Klugbauer N, Weizenegger M, Neumaier J et al. (1998). Bacterial phylogeny based on comparative sequence analysis. Electrophoresis 19: 554–568.
Ludwig W, Strunk O, Westram R, Richter L, Meier H, Yadhukumar et al. (2004). ARB: a software environment for sequence data. Nucleic Acids Res 32: 1363–1371.
Martinez RJ, Mills HJ, Story S, Sobecky PA . (2006). Prokaryotic diversity and metabolically active microbial populations in sediments from an active mud volcano in the Gulf of Mexico. Environ Microbiol 8: 1783–1796.
McIlroy S, Porter K, Seviour RJ, Tillett D . (2008). Simple and safe method for simultaneous isolation of microbial RNA and DNA from problematic populations. Appl Environ Microbiol 74: 6806–6807.
Mills HJ, Martinez RJ, Story S, Sobecky PA . (2005). Characterization of microbial community structure in Gulf of Mexico gas hydrates: comparative analysis of DNA- and RNA-derived clone libraries. Appl Environ Microbiol 71: 3235–3247.
Moeseneder MM, Arrieta JM, Herndl GJ . (2005). A comparison of DNA- and RNA-based clone libraries from the same marine bacterioplankton community. FEMS Microbiol Ecol 51: 341–352.
Moeseneder MM, Winter C, Herndl GJ . (2001). Horizontal and vertical complexity of attached and free-living bacteria of the eastern Mediterranean Sea, determined by 16S rDNA and 16S rRNA fingerprints. Limnol Oceanogr 46: 95–107.
Mohamed NM, Colman AS, Tal Y, Hill RT . (2008a). Diversity and expression of nitrogen fixation genes in bacterial symbionts of marine sponges. Environ Microbiol 10: 2910–2921.
Mohamed NM, Rao V, Hamann MT, Kelly M, Hill RT . (2008b). Monitoring bacterial diversity of the marine sponge Ircinia strobilina upon transfer into aquaculture. Appl Environ Microbiol 74: 4133–4143.
Mohamed NM, Saito K, Tal Y, Hill RT . (2009). Diversity of aerobic and anaerobic ammonia-oxidizing bacteria in marine sponges. ISME J, doi:10.1038/ismej.2009.84.
Morgenroth E, Obermayer A, Arnold E, Brühl A, Wagner M, Wilderer PA . (2000). Effect of long-term idle periods on the performance of sequencing batch reactors. Water Sci Technol 41: 105–113.
Poulsen LK, Ballard G, Stahl DA . (1993). Use of rRNA fluorescence in situ hybridization for measuring the activity of single cells in young and established biofilms. Appl Environ Microbiol 59: 1354–1360.
Pruesse E, Quast C, Knittel K, Fuchs BM, Ludwig W, Peplies J et al. (2007). SILVA: a comprehensive online resource for quality checked and aligned ribosomal RNA sequence data compatible with ARB. Nucleic Acids Res 35: 7188–7196.
Reiswig HM . (1981). Partial carbon and energy budgets of the bacteriosponge Verongia fistularis (Porifera: Demospongiae) in Barbados. PSZNI Mar Ecol 2: 273–293.
Rodriguez-Blanco A, Ghiglione J-F, Catala P, Casamayor EO, Lebaron P . (2009). Spatial comparison of total vs active bacterial populations by coupling genetic fingerprinting and clone library analyses in the NW Mediterranean Sea. FEMS Microbiol Ecol 67: 30–42.
Schloss PD, Handelsman J . (2005). Introducing DOTUR, a computer program for defining operational taxonomic units and estimating species richness. Appl Environ Microbiol 71: 1501–1506.
Schmitt S, Angermeier H, Schiller R, Lindquist N, Hentschel U . (2008). Molecular microbial diversity survey of sponge reproductive stages and mechanistic insights into vertical transmission of microbial symbionts. Appl Environ Microbiol 74: 7694–7708.
Schmitt S, Weisz JB, Lindquist N, Hentschel U . (2007). Vertical transmission of a phylogenetically complex microbial consortium in the viviparous sponge Ircinia felix. Appl Environ Microbiol 73: 2067–2078.
Sogin ML, Morrison HG, Huber JA, Welch DM, Huse SM, Neal PR et al. (2006). Microbial diversity in the deep sea and the underexplored ‘rare biosphere’. Proc Natl Acad Sci USA 103: 12115–12120.
Steger D, Ettinger-Epstein P, Whalan S, Hentschel U, de Nys R, Wagner M et al. (2008). Diversity and mode of transmission of ammonia-oxidizing archaea in marine sponges. Environ Microbiol 10: 1087–1094.
Taylor MW, Hill RT, Piel J, Thacker RW, Hentschel U . (2007a). Soaking it up: the complex lives of marine sponges and their microbial associates. ISME J 1: 187–190.
Taylor MW, Radax R, Steger D, Wagner M . (2007b). Sponge-associated microorganisms: evolution, ecology and biotechnological potential. Microbiol Mol Biol Rev 71: 295–347.
Taylor MW, Schupp PJ, Dahllof I, Kjelleberg S, Steinberg PD . (2004). Host specificity in marine sponge-associated bacteria, and potential implications for marine microbial diversity. Environ Microbiol 6: 121–130.
Thiel V, Neulinger SC, Staufenberger T, Schmaljohann R, Imhoff JF . (2007). Spatial distribution of sponge-associated bacteria in the Mediterranean sponge Tethya aurantium. FEMS Microbiol Ecol 59: 47–63.
Tringe SG, Hugenholtz P . (2008). A renaissance for the pioneering 16S rRNA gene. Curr Opin Microbiol 11: 442–446.
Troussellier M, Schafer H, Batailler N, Bernard L, Courties C, Lebaron P et al. (2002). Bacterial activity and genetic richness along an estuarine gradient (Rhone River plume, France). Aquat Microb Ecol 28: 13–24.
Vacelet J . (1975). Etude en microscopie electronique de l’association entre bacteries et spongiaires du genre Verongia (Dictyoceratida). J Microsc Biol Cell 23: 271–288.
Vacelet J, Donadey C . (1977). Electron microscope study of the association between some sponges and bacteria. J Exp Mar Biol Ecol 30: 301–314.
Wagner M, Horn M . (2006). The Planctomycetes, Verrucomicrobia, Chlamydiae and sister phyla comprise a superphylum with biotechnological and medical relevance. Curr Opin Biotechnol 17: 241–249.
Webster NS, Negri AP, Munro MM, Battershill CN . (2004). Diverse microbial communities inhabit Antarctic sponges. Environ Microbiol 6: 288–300.
Webster NS, Wilson KJ, Blackall LL, Hill RT . (2001). Phylogenetic diversity of bacteria associated with the marine sponge Rhopaloeides odorabile. Appl Environ Microbiol 67: 434–444.
Weisz JB, Lindquist N, Martens CS . (2008). Do associated microbial abundances impact marine demosponge pumping rates and tissue densities? Oecologia 155: 367–376.
West NJ, Obernosterer I, Zemb O, Lebaron P . (2008). Major differences of bacterial diversity and activity inside and outside of a natural iron-fertilized phytoplankton bloom in the Southern Ocean. Environ Microbiol 10: 738–756.
Wilkinson CR . (1983). Net primary productivity in coral reef sponges. Science 219: 410–412.
Wilkinson CR, Fay P . (1979). Nitrogen fixation in coral reef sponges with symbiotic cyanobacteria. Nature 279: 527–529.
Wilkinson CR, Summons RE, Evans E . (1999). Nitrogen fixation in symbiotic marine sponges: ecological significance and difficulties in detection. Mem Queensland Mus 44: 667–673.
Winter C, Moeseneder MM, Herndl GJ . (2001). Impact of UV radiation on bacterioplankton community composition. Appl Environ Microbiol 67: 665–672.
Zhu P, Li Q, Wang G . (2008). Unique microbial signatures of the alien Hawaiian marine sponge Suberites zeteki. Microb Ecol 55: 406–414.
Acknowledgements
We gratefully acknowledge the help of K Lau, G Lear and S Boycheva with RNA analyses, A Turner with TEM, M Mawdsley for assistance with sample collection, and P Deines (all University of Auckland) for helpful discussions. This research was supported by a University of Auckland New Staff Research Fund grant (Project: 9341 3609286) to MWT and a German Research Foundation (DFG) grant (SCHM 2559/1-1) to SS.
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Kamke, J., Taylor, M. & Schmitt, S. Activity profiles for marine sponge-associated bacteria obtained by 16S rRNA vs 16S rRNA gene comparisons. ISME J 4, 498–508 (2010). https://doi.org/10.1038/ismej.2009.143
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DOI: https://doi.org/10.1038/ismej.2009.143
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