Previous Article | Next Article ![]()
Applied and Environmental Microbiology, November 1999, p. 4926-4934, Vol. 65, No. 11
The Institute of Physical and Chemical Research (RIKEN) and
Japan Science and Technology Corporation (JST),
Received 12 July 1999/Accepted 27 August 1999
Nitrogen fixation by the microorganisms in the gut of termites is
one of the crucial aspects of symbiosis, since termites usually thrive
on a nitrogen-poor diet. The phylogenetic diversity of the
nitrogen-fixing organisms within the symbiotic community in the guts of
various termite species was investigated without culturing the resident
microorganisms. A portion of the dinitrogenase reductase gene
(nifH) was directly amplified from DNA extracted from the
mixed population in the termite gut. Analysis of deduced amino acid
sequences of the products of the clonally isolated nifH
genes revealed the presence of diverse nifH sequences in most of the individual termite species, and their constituents were
considerably different among termite species. A majority of the
nifH sequences from six lower termites, which showed
significant levels of nitrogen fixation activity, could be assigned to
either the anaerobic nif group (consisting of clostridia
and sulfur reducers) or the alternative nif methanogen
group among the nifH phylogenetic groups. In the case of
three higher termites, which showed only low levels of nitrogen
fixation activity, a large number of the sequences were assigned to the
most divergent nif group, probably functioning in some
process other than nitrogen fixation and being derived from
methanogenic archaea. The nifH groups detected were similar
within each termite family but different among the termite families,
suggesting an evolutionary trend reflecting the diazotrophic habitats
in the symbiotic community. Within these phylogenetic groups, the
sequences from the termites formed lineages distinct from those
previously recognized in studies using classical microbiological techniques, and several sequence clusters unique to termites were found. The results indicate the presence of diverse potentially nitrogen-fixing microbial assemblages in the guts of termites, and the
majority of them are as yet uncharacterized.
A symbiotic relationship between
termites and microorganisms inhabiting their gut enables termites to
live exclusively on lignocellulosic materials (4, 6).
Nitrogen fixation in termites is one of the crucial aspects of the
symbiosis, since the diet of termites is usually low in nitrogen
sources (1, 4, 5). The nitrogen fixation activity is
associated with the gut microorganisms. Ecologically, termites thrive
in great abundance and they play important roles in the turnover of
lignocellulose derived from dead plant materials. Considering their
great abundance, the ability of termites to fix atmospheric
N2 may also play a hitherto unrecognized role in
fertilization of ecosystems by replenishing combined nitrogen compounds. For example, it is known that termites are preyed upon by
various carnivores as important nitrogen sources (36, 41).
Termites are comprised of a complex assemblage of evolutionarily
diverse species, roughly divided into so-called lower and higher
termites (17). The lower termites, which comprise six families, harbor a dense and diverse population of both prokaryotes and
flagellated protists in their gut. The higher termites comprise only
one family but three-quarters of all termite species, and they also
harbor a dense and diverse array of prokaryotes. However, the higher
termites typically lack flagellated protists, and they have a more
elaborate morphology and social organization than do the lower
termites. The higher termites, especially, show considerable variation
in their feeding behavior, which is not limited to xylophagy. Some feed
exclusively on soil, presumably deriving nutrition from the humic
compounds therein, and others cultivate and consume cellulolytic fungi.
Even in the wood-feeding guilds, which include all lower termites, food
preferences range from sound to extensively decayed woods.
A wide variety of nitrogen fixation rates of termite species are known
(1, 4, 5). Within the same species, large variations in
nitrogen fixation rates have been demonstrated. At least one reason for
the variations is the nitrogen content of the termite diet fed prior to
the assay (5). Considering the variations in nitrogen-fixing
activity and the presence of evolutionarily diverse termite species,
differences in microbial populations and differences in the
constituents of the resident microorganisms responsible for nitrogen
fixation in the gut of termites are of significant interest and need to
be elucidated in order to understand the termite symbiotic systems.
Identification depending on culturing microorganisms may provide
limited information on the microbial diversity and the types of
organisms that fix nitrogen in termites, because only a few nitrogen-fixing microorganisms have been isolated from termites (12, 18, 31). Moreover, a majority of the members of the symbiotic community in the termite gut have been shown to be as yet
uncultivated microorganisms, as demonstrated by culture-independent analyses based on comparisons of PCR-amplified 16S rRNA genes (2,
24-27, 29, 33). However, a similar molecular approach, comparative analysis of a PCR-amplified nitrogen fixation gene, nifH, has provided evidence for a remarkable and previously
unexpected diversity of nitrogen-fixing microorganisms in the gut of
the lower termite Reticulitermes speratus (28).
The gene nifH encoding dinitrogenase reductase is
evolutionarily conserved and has often been used as the basis for
detecting nitrogen-fixing microorganisms in natural microbial
communities (3, 16, 34, 39, 40, 42, 43). Comparative
analysis of the nifH gene can provide information about the
phylogenetic identity of nitrogen-fixing organisms.
In this report, in an effort to compare the constituents of symbiotic
nitrogen-fixing microorganisms in the gut of evolutionarily diverse
termites, a portion of the nifH gene was PCR amplified and
characterized. The nifH sequences obtained were compared
among termite species. Phylogenetic analysis of the cloned
nifH sequences revealed that the diazotrophic populations in
the termite gut are far more diverse than previously recognized.
Termites and nitrogen fixation activity.
The termites
examined in this study and the time and place of sample collection are
shown in Table 1. Nitrogen fixation
activity was measured by the acetylene reduction assay (30).
Thirty to 200 live workers (or pseudergates) of the termite species
were placed in a stoppered 10-ml bottle containing 16%
C2H2. After incubation at room temperature for
1 to 3 h, a 0.1-ml gas sample was assayed for
C2H4 by using a flame ionization gas
chromatograph (Shimazu GC-14B) fitted with packed column J (3 mm by
1 m; GL Science) containing Porapak T (80/100 mesh). Helium was
the carrier gas (30 ml/min), and the column temperature was 50°C.
DNA extraction, PCR amplification, and cloning.
DNA was
extracted from the mixed population of microorganisms in the whole gut
of the termites as described previously (24, 26). The
nifH gene was amplified from the extracted DNA by PCR with
EX Taq DNA polymerase (Takara) according to the
manufacturer's instructions. The reaction conditions were 30 cycles of
94°C for 30 s, 48°C for 45 s, and 72°C for 2 min. The
PCR primers used were IGK and YAA (28), which are specific
for a portion of the nifH gene corresponding to amino acid
positions 11 to 165 of the Klebsiella pneumoniae nifH
sequence. The amino acid sequences of these two primers are the most
widely conserved sequences within nifH. PCR products of the
expected size (approximately 0.47 kb) were isolated by electrophoresis
by using a low-melting-point agarose gel (Seaplaque GTG; FMC
Bioproducts) and purified by means of the Wizard PCR prep DNA
purification system (Promega). In the case of Neotermes
koshunensis, the purified PCR product was cloned in pUC119 as
described previously (28). All of the other purified PCR
products were cloned in pGEM-T (Promega) according to the manufacturer's instructions.
FLT-RFLP analysis.
The primers used for the fluorescently
labeled terminal-restriction fragment length polymorphism (FLT-RFLP)
analysis were IGK-Cy5 (5'-TGYGAYCCNAARGCNGA-3' labeled at the 5' end
with Cy5; synthesized and purified by Pharmacia) and YAA. The reaction
conditions were the same as those for the standard PCR described above.
The products of the expected size were purified as described above and
then digested with HhaI. The lengths of the fluorescently labeled terminal restriction fragments from the PCR products were determined after electrophoresis by means of an automated sequencer, ALFred Express (Pharmacia), and analyzed by using Fragment Manager software (Pharmacia).
Nucleotide sequencing and phylogenetic analysis.
Plasmid
DNAs were prepared from randomly picked recombinant clones and used as
templates for sequencing performed by using the Dye Primer Cycle
Sequencing Kit (Applied Biosystems) with sequencing primers T7 and SP6
and an automatic sequence analyzer (Applied Biosystems model 377). The
names assigned to the clones are shown in Table
2. The previously determined
nifH sequences included in comparisons in this study were
retrieved from the GenBank, EMBL, and DDBJ nucleotide sequence
databases. Sequences were aligned by using the CLUSTAL W package
(38) and then corrected by manual inspection. Phylogenetic
analyses were restricted to unambiguously aligned amino acid residues.
The programs used to infer phylogenetic trees were those contained in
the PHYLIP package (11). PROTDIST with the Dayhoff PAM
matrix option was used to calculate evolutionary distances.
Phylogenetic trees were constructed from evolutionary distance data by
the neighbor-joining method (32), implemented through the
program NEIGHBOR. A total of 100 bootstrapped replicate resampling data
sets for PROTDIST were generated with the program SEQBOOT, to provide
confidence estimates for tree topologies (10).
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
Phylogenetic Diversity of Nitrogen Fixation Genes
in the Symbiotic Microbial Community in the Gut of Diverse
Termites
![]()
ABSTRACT
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
![]()
INTRODUCTION
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
![]()
MATERIALS AND METHODS
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References
TABLE 1.
Nitrogen fixation (C2H2
reduction) activity of termites examined in this study
TABLE 2.
Assignment of the nifH clones from the
symbiotic microbial community in the gut of termites to
phylogenetic groups
Nucleotide sequence accession numbers. The nifH sequences determined in this study will appear in the DDBJ, EMBL, and GenBank nucleotide sequence databases under accession no. AB011841 to AB011964.
| |
RESULTS |
|---|
|
|
|---|
Nitrogen fixation activity in diverse termites. Nitrogen fixation was measured in six lower termites and three higher termites by the acetylene reduction assay (Table 1). All six lower termites exhibited significant levels of nitrogen fixation activity. Among them, the highest activity was found in N. koshunensis. On the other hand, three higher termites, including a wood feeder (Nasutitermes takasagoensis), a fungus grower (Odontotermes formosanus), and a soil feeder (Pericapritermes nitobei), exhibited only low levels of activity.
FLT-RFLP analysis of the amplified nifH genes. In the six lower termites which exhibited relatively high levels of nitrogen fixation activity, the variation in the amplified nifH sequences was examined and the sequences were compared among the termite species by FLT-RFLP analysis (Fig. 1). This technique is based on RFLP analysis but it differs from conventional RFLP analysis in that a single fluorescent fragment from one terminal side forms the sole focus of the analysis, in contrast to the profile of multiple fragments in RFLP analysis (7, 21). In FLT-RFLP analysis of PCR-amplified DNA from a mixed population, the single fragment length corresponds to a unique sequence or a subclass of sequences. Thus, this technique is expected to be useful for measuring sequence variation and comparing community structures in the ecosystems under investigation. In most of the lower termites, a remarkable diversity of the amplified nifH sequences was detected. Although some terminal restriction fragments (T-RFs) were common among several termites, the profiles of the T-RFs were quite dissimilar among the termite species. The results indicated that the nitrogen fixation genes within the members of the symbiotic microbial community in the termite gut were significantly different among the various termite species. Thus, we decided to further analyze the amplified nifH sequences by cloning and sequencing.
|
Cloning and analysis of nifH sequences. The nucleotide sequences of around 24 clones in our libraries of nifH sequences were analyzed for each termite species. We found several completely identical DNA sequences and completely identical amino acid sequences within the library of a single termite species (Table 2). Completely identical amino acid sequences were also encountered four times in comparisons between different termite species: between NKN12 and RSN-TKY19 (in this case, the nucleotide sequence was also identical), NKN9 and OFN35, GFN8 and PNN16, and OFN1 and PNN31. From eight termite species, 125 different nucleotide sequences which encoded 92 different amino acid sequences were newly identified in this study (these numbers do not include the previously reported sequences from R. speratus [28]). These results indicate that notably heterogeneous nitrogenase sequences are present in the symbiotic microbial community in the gut of termites, and most of them are different between termite species.
As shown in Fig. 1, the amplified nifH sequences derived from H. sjoestedti exhibited low heterogeneity in the T-RFs. In fact, a majority of the nifH clones from H. sjoestedti (22 of 24) shared predicted T-RFs of identical length and shared high sequence similarity (less than two amino acids difference). In the case of the other termites, most of the dominant T-RFs detected could be assigned to isolated clones. The sequences corresponding to the T-RFs of 57 and 143 bases in Coptotermes formosanus and that of 65 bases in Cryptotermes domesticus could not be identified, suggesting that further sampling of clones in these termites should give more diversity of nifH sequences.Phylogenetic locations. The nifH amino acid sequences from the termites were compared with each other and with sequences in the databases, and their phylogenetic relationships were investigated. Figure 2 shows a large phylogenetic tree representing four major groups of nifH sequences; the proteobacteria-cyanobacteria (proteo-cyano) group, the anaerobe group, the alternative nif methanogen (anf-methano) group, and the pseudo nif group. These four groups corresponded to the previously recognized group of nifH phylogeny (8). As described previously (8) and in this report (see below), the pseudo nif group is the most divergent nif group and is considered to function in some process other than nitrogen fixation. nifH sequences from the termites are present in each of the four groups; however, the majority of the sequences belong to three of the four groups, the anaerobe group, the anf-methano group, and the pseudo nif group. Table 2 summarizes the number of clones in each phylogenetic group detected (see below). The nifH sequences from termites were not dispersed among the nifH sequences described thus far; instead, most of the termite sequences seemed to form several sequence clusters (Fig. 2).
|
- and
-proteobacteria clusters is most closely
related to the sequences of Azoarcus spp. within the
-proteobacteria cluster (14), especially to that of
Azoarcus indigens (94.7% amino acid identity). The NKN19
sequence showed significant similarity (90.9% amino acid identity)
with the sequence of nifH derived from zooplankton in the
Gulf of Mexico (GM24) (42). They also shared a unique
sequence feature, a 12-amino-acid residue insertion (42),
suggesting the presence of related nitrogen-fixing organisms in both
the termite and the zooplankton. The NKN19 sequence seemed to root with
the
-proteobacteria cluster; however, analysis of the zooplankton sequence led to its placement in the
-proteobacteria cluster (42). Since NKN19 and the zooplankton sequence are deeply
branched within the proteo-cyano group, the identity of these organisms is difficult to predict. The nucleotide sequences of each of the other
two clones derived from N. koshunensis were found to be identical to NKN19.
Anaerobe nif group. Figure 3 shows the phylogenetic relationships of the nifH sequences in the anaerobic group, which includes sequences from clostridia, sulfate reducers, and Methanosarcina barkeri 227. The termite-derived nifH sequences formed three clusters (clusters I to III). Two large clusters (I and II), which corresponded to termite clusters I and II in the previous analysis of nifH sequences derived from R. speratus, respectively (28), are related to sequences from clostridia, Clostridium pasteurianum and Clostridium cellobioparum. Cluster II, especially, includes the sequence from C. cellobioparum, suggesting that the sequences belonging to this cluster may be derived from clostridia. Cluster I, however, consists only of the termite sequences and forms a distinct lineage within the anaerobe nif group, indicating the presence of unique nitrogen-fixing microorganisms in termites. Also, the third cluster (III) includes no sequences related to those of cultivated organisms. The sequences in cluster III are related to a sequence from rice roots that was amplified by PCR without cultivation of the resident microorganism (39), suggesting the presence of similar diazotrophic habitats in both ecosystems. Other than the sequences within these three clusters, there were also two minor clusters consisting only of a few sequences. The sequences CDN28 and RSN-TDY3 clustered together and are related to that of Desulfovibrio gigas (83.9 and 83.5% amino acid identity, respectively). These two sequences are somewhat related to those from marine environments, especially zooplankton (copepod)-associated sequences (3, 42). As discussed previously (3, 42), similar diazotrophic anaerobes might inhabit the guts of both invertebrates. Three sequences derived from termites, CDN14, NTN30, and RSN-TKG3, were grouped together with nifH2 of M. barkeri 227, although the grouping was not supported by bootstrap analysis. The presence of methanogenic archaea in the termite gut is well known (19, 20, 26, 27, 33); thus, these sequences are presumed to originate from gut methanogens.
|
anf-methano group. Figure 4 shows the phylogenetic relationships of the nifH sequences in the anf-methano group. Most of the sequences in this group are derived from termites of the families Kalotermitidae and Termopsidae. Two clusters (designated as anf-methano clusters I and II) comprised only of termite-derived sequences are present in this group, and the clustering was supported by high bootstrap values (100 and 92%, respectively). Except for NKN23, all of the termite-derived sequences in the anf-methano group belong to one of these two clusters. The members of anf-methano clusters I and II share more than 94 and 91% amino acid identity, respectively, in clear contrast with the lower rates of relatedness among members of the clusters in the anaerobe groups. This observation indicates that these sequences are derived from closely related organisms and that they are shared among several termite species. The sequences from organisms in the domain Bacteria seem to form a monophyletic lineage in the anf-methano group, although the monophyly was not supported by bootstrap analysis. This lineage contains all of the termite-derived sequences in the anf-methano group, suggesting their eubacterial origin. However, the identity of the corresponding nitrogen-fixing microorganisms could not be predicted because the branching order was unstable and not supported by bootstrap analysis. anf-methano cluster II includes most of the sequences derived from H. sjoestedti (22 of 24), indicating that the microorganisms represented by them are a major population in diazotrophic habitats in the gut and thus are responsible for nitrogen fixation in H. sjoestedti.
|
Pseudo nif group. Figure 5 shows the phylogenetic relationships of the nifH sequences in the pseudo nif group, which is deeply branched in the large nifH phylogenetic tree (Fig. 1). The known members of this group were derived from methanogenic archaea and were considered to function in some process other than nitrogen fixation. Most of the sequences derived from the higher termites, especially those from O. formosanus and P. nitobei, were assigned to the archaea group. The sequences from the termites form four clusters within this group (designated as pseudo nif clusters I to IV), which were significantly supported by bootstrap analysis (62, 100, 77, and 98% support, respectively). Most of the members of cluster I are sequences derived from lower termites. All four sequences in cluster II are derived from the higher termites O. formosanus and P. nitobei. A majority of the sequences from O. formosanus (17 of 24) were found to be identical to OFN1 in cluster II. Clusters III and IV seem to be somewhat related; however, the grouping was not supported by bootstrap analysis. Cluster IV consists of the most diverse sequences but includes the nifH sequence of M. barkeri DSM800, suggesting that the sequences in this cluster may have originated from Methanosarcina-related organisms.
|
| |
DISCUSSION |
|---|
|
|
|---|
The nitrogen fixation gene nifH was isolated from members of the symbiotic microbial community in the gut of evolutionarily diverse termites by a culture-independent approach and analyzed phylogenetically. Remarkably diverse nifH sequences were isolated from each termite species, and most of the nifH sequences were found to be novel and distantly related to those of cultivated organisms or as yet unidentified organisms detected in other environments (3, 34, 39, 40, 42, 43). The results indicate the presence of potential diazotrophic habitats of unexpected diversity in the gut of termites, which are as yet unidentified and uncharacterized. Notably, identical nifH amino acid sequences were scarcely isolated from different termite species (only four times). The more termite species we investigated, the more distinct were the nifH sequences isolated. Given the existence of more than 2,000 described species on the earth, termites may be a rich reservoir of novel and diverse microorganisms that potentially fix nitrogen.
Several species of nitrogen-fixing bacteria, including
Citrobacter freundii, Enterobacter agglomerans,
and Desulfovibrio spp., have been isolated from the gut of
termites (12, 18, 31). The first two belong to the
subclass of proteobacteria, and the termite-derived sequences RSN-TKY17
and NKN19 were assigned to proteobacteria nifH clusters. The
sequences RSN-TDY3 and CDN28 are related to the nifH
sequence of D. gigas. Although the nifH genes of
bacterial isolates from termites have not been characterized, these
sequences may originate from organisms related to them. However, the
number of clones found to have these sequences was relatively few,
suggesting that these represent minor populations in the termite gut.
On the other hand, the organisms presumably corresponding to the
remaining clusters and/or sequences, which comprise the majority of the
isolated sequences, have not yet been identified or cultivated from
termites as nitrogen fixers. The isolation of organisms related to
clostridia and methanogens from the gut of termites has been reported
(13, 15, 19, 20), but their nitrogen-fixing ability has not
been reported. Thus, we have little knowledge of the organisms
responsible for nitrogen fixation in termites.
The nifH sequences isolated from the termites form several unique clusters in the phylogenetic trees. They are not randomly distributed over the nifH taxa. Some particular types of nitrogen-fixing microorganisms probably inhabit the gut of termites. Notably, sequences affiliated with the proteo-cyano group were found to occur very rarely in the termite gut. Since the proteobacteria are believed to comprise a substantial proportion of the gut microbial community (24) and since most of the nitrogen-fixing organisms isolated from the gut of termites are proteobacteria (12, 31), the extremely low abundance of their nifH sequences was unexpected. The finding that the minority of termite-derived nifH sequences were clustered in the proteo-cyano group is in striking contrast to the results of studies on nifH sequences derived from other natural environments, such as those from the picoplankton-size fraction of oligotrophic oceans (42) and those from soil and litter in a Douglas fir forest (40), where nifH sequences of the proteo-cyano group are rather predominant. The presence of large numbers of heterogeneous sequences clustering in the anaerobe group is common in several environments, such as in the termite gut (this study and reference 28), rice roots (39), marine cyanobacterial mats (43), and enrichment cultures initiated with marine zooplankton (3), though clustering in the proteo-cyano group was observed also in the study of rice roots. However, a majority of the termite-derived sequences in the anaerobe group form lineages distinct from those derived from other environments (e.g., termite anaerobe clusters I and II). These features may reflect differences in diazotrophic habitats dependent on the microbial ecosystems. Above all, the most striking and distinctive feature of the sequences from the other environments was the presence of those affiliated with the anf-methano group in the gut of some termites. The anf sequences have never been found in any other environment. The alternative nitrogenase encoded by the anf gene differs from conventional nitrogenases in terms of its metal components serving as cofactors (9). The alternative nitrogenase contains neither molybdenum nor vanadium and is expressed under conditions of molybdenum depletion. Metal availability probably is a key factor determining the presence of nitrogen fixation genes of the anf-methano group (discussed also in reference 23).
Only low levels of nitrogen fixation activity were detected in higher termites (Table 1). Of course, our experimental conditions might not be adequate to obtain optimal activity. For example, there was an interval of several days between the time of sample collection (the removal of termites from their nests) and the assay, and they cannot be kept alive in vitro for a long time after removal from their nests. In fact, a significant level of C2H2 reduction activity (up to 50 nmol of C2H4 formed per h per g [wet weight]) has been demonstrated in the case of the wood-feeding higher termite N. takasagoensis (22). However, little activity was found in the soil-feeding termite P. nitobei or the fungus-growing termite O. formosanus (22). Based on the results of stable isotope analyses in studies of both soil-feeding and fungus-growing higher termites, nitrogen fixation appears to contribute less to their nitrogen economy than in the case of wood-feeding termites (35-37). As discussed previously, the feeding habits and foraging preferences may obviate the need for nitrogen fixation simply because their diet contains an adequate amount of combined nitrogen (4).
In spite of the low levels of nitrogen fixation activity displayed by the higher termites examined here, various nifH sequences were isolated from them. A large proportion of the sequences isolated from the higher termites, especially from P. nitobei and O. formosanus, were assigned to the pseudo nif group. The results suggest that the product of the nifH gene in the pseudo nif group may not be a functional nitrogenase. It has been suggested previously that it may encode a product that is not a nitrogenase based on the following criteria: their high degree of divergence relative to other nifH groups; their lack of nifD- or glnB-like open reading frames, found downstream from them; the inability by some members in this group (Methanococcus voltae and Methanococcus jannaschii) to detect nitrogen fixation; their expression in Methanococcus thermolithotrophicus; and their significant sequence similarity with the iron proteins involved in bacteriochlorophyll synthesis (reference 8 and the references therein). The variation in the nifH sequences can be simply explained by the variation in the methanogen species present, since it has been reported that phylogenetically there is a greater variety of methanogen species in the gut of higher termites than in the gut of lower termites (27). The dominance of the clones in this group probably reflects the absence of functional nitrogenase genes within the gut community.
In N. takasagoensis, nifH sequences in the anaerobe group as well as those in the pseudo nif group were present, although the level of nitrogen fixation activity was very low. The results imply that the existence of nifH sequences does not simply lead to active nitrogen fixation. Since nitrogenases are strictly regulated at the transcriptional and posttranslational levels (9), further analysis of the expression of nifH will be necessary in order to determine whether the gene is functional in these organisms and their contribution to nitrogen fixation in termites. Even in those termites showing high levels of activity, whether the nifH sequences detected are really responsible for nitrogen fixation in termites remains to be clarified. In fact, we have shown that only restricted groups of the nifH sequences are preferentially expressed in N. koshunensis, as determined by analyzing the levels of nifH mRNA in the microbial population in the gut (23). Still, the potential nifH phylotypes described here will serve as an important basis for further studies.
Interestingly, some phylogenetic relationships between the termite families and the nifH groups of symbiotic microorganisms are evident (Table 2). In the higher termites, which are phylogenetically related and assembled into a single termite family, Termitidae, the majority of the nifH sequences were assigned to the pseudo nif group. In the lower termites, the number of clones of nifH sequences belonging to the pseudo nif group was few. Many of the nifH sequences assigned to the anaerobe group were isolated from termites of the family Rhinotermitidae, and those belonging to the anf-methano group were never found in this termite family. From the three members of the family Kalotermitidae, sequences assigned to either the anaerobe group or the anf-methano group were isolated in large numbers. The sequences in the anf-methano group are exclusively derived from termites of either the family Kalotermitidae or the family Termopsidae. Surprisingly, all of the nifH sequences from H. sjoestedti (family Termopsidae) were exclusively assigned to cluster II of the anf-methano group, with only one exception. Of course, more analyses with more diverse termites are necessary to reach any definitive conclusion. Nevertheless, these relationships are suggestive of the evolution of the symbiosis between termites and their nitrogen-fixing inhabitants. Alternatively, these relationships can be simply explained in terms of the nutritional ecology of the termites, since their feeding behavior differs somewhat. The three termites of the family Kalotermitidae feed on dry and sound wood. The termites of the family Rhinotermitidae are known to be subterranean termites, whereas the termites of the family Termopsidae are known as damp wood termites. The factors affecting the choice of termites as diazotrophic habitats by symbionts are as yet uncertain and remain to be clarified.
The culture-independent approach applied here has revealed that the major population responsible for nitrogen fixation in the gut of termites is a population of as yet uncharacterized microorganisms. The nifH sequence was found to be a useful means of detecting them and predicting their taxonomy. Since cloning and sequencing are laborious tasks, FLT-RFLP analysis may serve as a simpler but significantly informative technique for surveying community structures as demonstrated in this study. Now that we have sequence data on nifH genes from nine evolutionarily diverse termites, we can predict the presence of a particular class of nitrogenase genes within the microbial community in the termite gut, depending on the presence of certain T-RFs in the FLT-RFLP analysis. For example, the T-RFs of 161 and 172 bases are exclusively derived from the nifH sequences in the anf-methano group, and the T-RFs of 259 and 307 bases are derived from those in the anaerobe group. However, since PCR amplification may introduce some biases with respect to the gene composition of the products, a quantitative approach is necessary to measure real populations in the original sample. The nifH sequence data described in this study will allow us to design sequence-specific probes and/or primers for specific detection, hybridization, and quantitative experiments. Although isolation and cultivation of the corresponding microorganisms are advantageous for taxonomic and physiological characterization in detail, culture-independent approaches will provide valuable information about the nitrogen economy and the ecology within the symbiotic community in the gut of termites.
| |
ACKNOWLEDGMENTS |
|---|
This work was partially supported by grants from the Biodesign Research Program, the Genome Research Program, and the Eco Molecular Science Research Program from RIKEN and by a grant from the International Cooperative Research Project (Bio-Recycle Project) from Japan Science and Technology Corporation. S.N. was supported by a grant from the Junior Research Associate Program from RIKEN.
We thank F. Aoki for assistance and I. Yasuda for advice on termite collection.
| |
FOOTNOTES |
|---|
* Corresponding author. Mailing address: Microbiology Laboratory, RIKEN (The Institute of Physical and Chemical Research), Hirosawa 2-1, Wako, Saitama 351-0198, Japan. Phone: 81-48-462-1111, ext. 5724. Fax: 81-48-462-4672. E-mail: mohkuma{at}mailman.riken.go.jp.
| |
REFERENCES |
|---|
|
|
|---|
| 1. |
Benemann, J. R.
1973.
Nitrogen fixation in termites.
Science
181:164-165 |
| 2. | Berchtold, M., and H. König. 1996. Phylogenetic analysis and in situ identification of uncultivated spirochetes from the hindgut of the termite Mastotermes darwiniensis. Syst. Appl. Microbiol. 19:66-73. |
| 3. | Braun, S. T., L. M. Proctor, S. Zani, M. T. Mellon, and J. P. Zehr. 1999. Molecular evidence for zooplankton-associated nitrogen-fixing anaerobes based on amplification of the nifH gene. FEMS Microbiol. Ecol. 28:273-279. |
| 4. | Breznak, J. A. 1982. Intestinal microbiota of termites and other xylophagous insects. Ann. Rev. Microbiol. 36:323-343[Medline]. |
| 5. | Breznak, J. A., W. J. Brill, J. W. Mertins, and H. C. Coppel. 1973. Nitrogen fixation in termites. Nature 244:577-580[Medline]. |
| 6. | Breznak, J. A., and A. Brune. 1994. Role of microorganisms in the digestion of lignocellulose by termites. Ann. Rev. Entomol. 39:453-487. |
| 7. | Bruce, K. D. 1997. Analysis of mer gene subclasses within bacterial communities in soils and sediments resolved by fluorescent-PCR restriction fragment length polymorphism profiling. Appl. Environ. Microbiol. 63:4914-4919[Abstract]. |
| 8. |
Chien, Y.-T., and S. H. Zinder.
1994.
Cloning, DNA sequencing, and characterization of a nifD-homologous gene from the archaeon Methanosarcina barkeri 227 which resembles nifD1 from the eubacterium Clostridium pasteurianum.
J. Bacteriol.
176:6590-6598 |
| 9. | Dean, D. R., and M. R. Jacobson. 1992. Biochemical genetics of nitrogenase, p. 763-834. In G. Stacy, R. H. Burris, and H. J. Evans (ed.), Biological nitrogen fixation. Chapman and Hall, New York, N.Y |
| 10. | Felsenstein, J. 1985. Confidence limits on phylogenies: an approach using the bootstrap. Evolution 39:783-791. |
| 11. |
Felsenstein, J.
1989.
PHYLIP phylogeny inference package version 3.5.
Cladistics
5:164-166.
|
| 12. | French, J. R. J., G. L. Turner, and J. F. Bradbury. 1976. Nitrogen fixation by bacteria from the hindgut of termite. J. Gen. Microbiol. 95:202-206. |
| 13. | Hethener, P., A. Brauman, and J.-L. Garcia. 1992. Clostridium termitidis sp. nov., a cellulolytic bacterium from the gut of the wood-feeding termite, Nasutitermes lujae. Syst. Appl. Microbiol. 15:52-58. |
| 14. |
Hurek, T.,
T. Egener, and B. Reinhold-Hurek.
1997.
Divergence in nitrogenase of Azoarcus spp., proteobacteria of the subclass.
J. Bacteriol.
179:4172-4178 |
| 15. | Kane, M. D., A. Brauman, and J. A. Breznak. 1991. Clostridium mayombei sp. nov., an H2/CO2 acetogenic bacterium from the gut of the African soil-feeding termite, Cubitermes speciosus. Arch. Microbiol. 156:99-104. |
| 16. |
Kirshtein, J. D.,
H. W. Paerl, and J. Zehr.
1991.
Amplification, cloning, and sequencing of a nifH segment from aquatic microorganisms and natural communities.
Appl. Environ. Microbiol.
57:2645-2650 |
| 17. | Krishna, K. 1970. Taxonomy, phylogeny and distribution of termites, p. 127-152. In K. Krichna, and F. M. Weesner (ed.), Biology of termites, vol. 2. Academic Press, Inc., New York, N.Y |
| 18. | Kuhniugk, T., J. B. D. Krekeler, H. Cypionka, and H. König. 1996. A feasible role of sulfate-reducing bacteria in the termite gut. Syst. Appl. Microbiol. 19:139-149. |
| 19. | Leadbetter, J. R., and J. A. Breznak. 1996. Physiological ecology of Methanobrevibacter cuticularis sp. nov., and Methanobrevibacter curvatus sp. nov., isolated from the hindgut of the termite Reticulitermes flavipes. Appl. Environ. Microbiol. 62:3620-3631[Abstract]. |
| 20. | Leadbetter, J. R., L. D. Crosby, and J. A. Breznak. 1998. Methanobrevibacter filiformis sp. nov., a filamentous methanogen from termite hindguts. Arch. Microbiol. 169:287-292[Medline]. |
| 21. | Liu, W.-T., T. L. Marsh, H. Cheng, and L. J. Forney. 1997. Characterization of microbial diversity by determining terminal restriction fragment length polymorphisms of genes encoding 16S rRNA. Appl. Environ. Microbiol. 63:4516-4522[Abstract]. |
| 22. | Nakamura, T., and K. Yara. Unpublished data. |
| 23. |
Noda, S.,
M. Ohkuma,
R. Usami,
K. Horikoshi, and T. Kudo.
1999.
Culture-independent characterization of a gene responsible for nitrogen fixation in the symbiotic microbial community in the gut of the termite Neotermes koshunensis.
Appl. Environ. Microbiol.
65:4935-4942 |
| 24. | Ohkuma, M., and T. Kudo. 1996. Phylogenetic diversity of the intestinal bacterial community in the termite Reticulitermes speratus. Appl. Environ. Microbiol. 62:461-468[Abstract]. |
| 25. | Ohkuma, M., and T. Kudo. 1998. Phylogenetic analysis of the symbiotic intestinal microflora of the termite Cryptotermes domesticus. FEMS Microbiol. Lett. 164:389-395. |
| 26. | Ohkuma, M., S. Noda, K. Horikoshi, and T. Kudo. 1995. Phylogeny of symbiotic methanogens in the gut of the termite Reticulitermes speratus. FEMS Microbiol. Lett. 134:45-50[Medline]. |
| 27. | Ohkuma, M., S. Noda, and T. Kudo. 1999. Phylogenetic relationships of symbiotic methanogens in diverse termites. FEMS Microbiol. Lett. 171:147-153[Medline]. |
| 28. | Ohkuma, M., S. Noda, R. Usami, K. Horikoshi, and T. Kudo. 1996. Diversity of nitrogen fixation genes in the symbiotic intestinal microflora of the termite Reticulitermes speratus. Appl. Environ. Microbiol. 62:2747-2752[Abstract]. |
| 29. | Paster, B. J., F. E. Dewhirst, S. M. Cooke, V. Fussing, L. K. Poulsen, and J. A. Breznak. 1996. Phylogeny of not-yet-cultured spirochetes from termite guts. Appl. Environ. Microbiol. 62:347-352[Abstract]. |
| 30. | Postgate, J. R. 1972. The acetylene reduction test for nitrogen fixation, p. 343-356. In J. R. Norris, and D. W. Ribbons (ed.), Methods in microbiology, vol. 6B. Academic Press, Inc., New York, N.Y |
| 31. |
Potrikus, C. J., and J. A. Breznak.
1977.
Nitrogen-fixing Enterobacter agglomerans isolated from guts of wood-eating termites.
Appl. Environ. Microbiol.
33:392-399 |
| 32. | Saiton, N., and M. Nei. 1987. The neighbor-joining method: a new method for reconstructing phylogenetic trees. Mol. Biol. Evol. 4:406-425[Abstract]. |
| 33. |
Shinzato, N.,
T. Matsumoto,
I. Yamaoka,
T. Oshima, and A. Yamagishi.
1999.
Phylogenetic diversity of symbiotic methanogens living in the hindgut of the lower termite Reticulitermes speratus analyzed by PCR and in situ hybridization.
Appl. Environ. Microbiol.
65:837-840 |
| 34. | Steppe, T. F., J. B. Olson, H. W. Paerl, R. W. Litaker, and J. Belnap. 1996. Consortial N2 fixation: a strategy for meeting nitrogen requirements of marine and terrestrial cyanobacterial mats. FEMS Microbiol. Ecol. 21:149-156. |
| 35. | Tayasu, I., T. Abe, P. Eggleton, and D. E. Bignell. 1997. Nitrogen and carbon isotope ratios in termites: an indicator of trophic habit along the gradient from wood-feeding to soil-feeding. Ecol. Entomol. 22:343-351. |
| 36. | Tayasu, I., T. Inoue, L. R. Miller, A. Sugimoto, S. Takeichi, and T. Abe. 1998. Confirmation of soil-feeding termites (Isoptera; Termitidae; Termitinae) in Australia using stable isotope ratios. Funct. Ecol. 12:536-542. |
| 37. | Tayasu, I., A. Sugimoto, E. Wada, and T. Abe. 1994. Xylophagous termites depending on atmospheric nitrogen. Naturwissenschaften 81:229-231. |
| 38. |
Thompson, J. D.,
D. G. Higgins, and T. J. Gibson.
1994.
CLUSTAL W: improving the sensitivity of progressive multiple sequence alignment through sequence weighting, position-specific gap penalties and weight matrix choice.
Nucleic Acids Res.
22:4673-4680 |
| 39. |
Ueda, T.,
Y. Suga,
N. Yahiro, and T. Matuguchi.
1995.
Remarkable N2-fixing bacterial diversity detected in rice roots by molecular evolutionary analysis of nifH gene sequences.
J. Bacteriol.
177:1414-1417 |
| 40. |
Widmer, F.,
B. T. Shaffer,
L. A. Porteous, and R. J. Seidler.
1999.
Analysis of nifH gene pool complexity in soil and litter at a Douglas fir forest site in the Oregon Cascade mountain range.
Appl. Environ. Microbiol.
65:374-380 |
| 41. | Wood, T. G., and W. A. Sand. 1978. The role of termites in ecosystems, p. 245-292. In M. V. Brian (ed.), Production ecology of ants and termites. Cambridge University Press, Cambridge, England |
| 42. |
Zehr, J. P.,
M. T. Mellon, and S. Zani.
1998.
New nitrogen-fixing microorganisms detected in oligotrophic oceans by amplification of nitrogenase (nifH) genes.
Appl. Environ. Microbiol.
64:3444-3450 |
| 43. | Zehr, J. P., M. Mellon, S. Braun, W. Litaker, T. Steppe, and H. W. Paerl. 1995. Diversity of heterotrophic nitrogen fixation genes in a marine cyanobacterial mat. Appl. Environ. Microbiol. 61:2527-2532[Abstract]. |
This article has been cited by other articles:
| |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Copyright © 2009 by the American Society for Microbiology. For an alternate route to Journals.ASM.org, visit: http://intl-journals.asm.org | More Info»