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Applied and Environmental Microbiology, July 2001, p. 3002-3009, Vol. 67, No. 7
Department of Biology, University of Oregon,
Eugene, Oregon 97403
Received 11 January 2001/Accepted 11 April 2001
Synechococcus sp. strain SH-94-5 is a nitrate
assimilation-deficient cyanobacterium which was isolated from an
ammonium-replete hot spring in central Oregon. While this clone could
grow on ammonium and some forms of organic nitrogen as sole nitrogen
sources, it could not grow on either nitrate or nitrite, even under
conditions favoring passive diffusion. It was determined that this
clone does not express functional nitrate reductase or nitrite
reductase and that the lack of activity of either enzyme is not due to
inactivation of the cyanobacterial nitrogen control protein NtcA. A few
other naturally occurring cyanobacterial strains are also nitrate
assimilation deficient, and phylogenetic analyses indicated that the
ability to utilize nitrate has been independently lost at least four
times during the evolutionary history of the cyanobacteria. This
phenotype is associated with the presence of environmental ammonium, a
negative regulator of nitrate assimilation gene expression, which may
indicate that natural selection to maintain functional copies of
nitrate assimilation genes has been relaxed in these habitats. These
results suggest how the evolutionary fates of conditionally expressed genes might differ between environments and thereby effect ecological divergence and biogeographical structure in the microbial world.
In the cyanobacteria, nitrogen (N)
comprises approximately 10% of cell dry weight (9). These
oxygen-evolving, photoautotrophic bacteria primarily use inorganic N
sources to meet their nutritional requirements, of which nitrate is
generally the most available form of combined N (19).
Nitrate is actively transported across the cell membrane by either an
ATP-binding cassette transporter or a nitrate permease
(45), and once inside the cell, it is sequentially reduced
to nitrite and ammonium through the activities of nitrate reductase
(Nar) and nitrite reductase (Nir), respectively (9, 35).
The eight electrons required to reduce nitrate to ammonium are donated
by photosynthetically reduced ferredoxin (30), and
ammonium is subsequently incorporated into amino acids, primarily via
the glutamine synthetase (GS)-glutamate synthase cycle
(31).
The genes encoding the ATP-binding cassette transporter
(nrtABCD), Nar (narB), and Nir (nirA)
cluster as a similarly organized, cotranscribed unit (the
nirA operon) in Synechococcus sp. strain PCC 7942 (35) and Anabaena sp. strain PCC 7120 (12). However, differences in the genetic organization of
nitrate assimilation genes have been described for
Synechocystis sp. strain PCC 6803 (22) and
Phormidium laminosum (32). Despite these
differences in genetic architecture, cyanobacteria regulate the
expression of nitrate assimilation genes in a similar manner. These
organisms preferentially use ammonium if it is available, presumably
because it can be directly incorporated into organic matter without the associated costs of reducing the power required for the utilization of
other forms of inorganic N (9). While ammonium has been shown to posttranslationally inhibit nitrate transport in
Anacystis nidulans PCC 6301 (26), the principal
way ammonium regulates nitrate utilization in cyanobacteria is by
negative transcriptional control of nitrate assimilation gene
expression (29). Transcription is derepressed in the
absence of ammonium but must be activated by the cyanobacterial N
control protein NtcA, a member of the Crp family of DNA-binding
proteins (44).
Genes which are conditionally expressed may evolve with different
dynamics in different environmental contexts and therefore provide the
raw material for ecological diversification. Here we report the
isolation in laboratory culture of a nitrate assimilation-deficient clone of the thermophilic cyanobacterium Synechococcus
from an ammonium-rich hot spring in central Oregon. We characterized
the N sources which support its growth and investigated possible
mechanisms by which the ability to use nitrate may have been lost in
this clone. While this phenotype is rare among cyanobacterial isolates, it is exhibited by a few other strains from diverse habitats. We first
inferred the phylogenetic distribution of this phenotype among
cyanobacteria to evaluate whether the loss of the ability to assimilate
nitrate has a single or multiple evolutionary origins. We further
identified an apparent association between the evolution of this trait
and the presence of environmental ammonium and discussed the
potential biogeographical implications of this association.
Isolation and culture maintenance.
The inoculum was a
microbial mat sample collected from an area with a temperature of
50°C in the main channel of South Harney Hot Springs, a slightly
alkaline (pH 7.4) spring located near the southern end of Harney Lake,
Harney County, Oreg. The cyanobacterial cell density of a homogenized
suspension was quantified with a hemocytometer, and aliquots containing
an estimated five cyanobacterial cells were delivered to flasks of
BG11, D, and NT media (5) and incubated under low cool
white fluorescent light at 45°C. An axenic isolate
(Synechococcus sp. strain SH-94-5) was obtained from an NT
enrichment flask after repeated streakings on 1.5% agar plates and
incubating as described above. SH-94-5 was maintained under the above
conditions both on plates and in flasks of NDA medium [N-free ND
medium (5) supplemented with 0.38 mM
(NH4)2S2O4 and 0.4 mM
Na2S2O3 · 5H2O], which contains ammonium as the sole utilizable N
source. The addition of sodium thiosulfate has been found to improve
the survival and growth of many cyanobacteria isolated from hot spring
environments replete with reduced sulfur and nitrogen (5).
This strain has been deposited in the Culture Collection of
Microorganisms from Extreme Environments at the University of Oregon
(strain CCMEE-5231).
N sources supporting growth.
SH-94-5 was screened for growth
on a number of N sources. For all treatments, duplicate flasks were
incubated at 45°C with 100 microeinsteins of cool white fluorescent
light m Reversion assay.
Ammonium-grown SH-94-5 cells starved for N
for 60 h were washed in ND medium, centrifuged, and resuspended in
ND medium to a final density of 109 cells
ml Nar and Nir assays.
Nar activity was assayed as nitrate
reduction (with sodium dithionite-reduced methyl viologen as the
electron donor) by cells permeabilized with mixed alkyl
trimethylammonium bromide at a final concentration of 75 µg
ml
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.7.3002-3009.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Ecological Physiology of Synechococcus
sp. Strain SH-94-5, a Naturally Occurring Cyanobacterium Deficient
in Nitrate Assimilation
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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
2 s
1 in ND medium supplemented with
100 mg of Na2S2O3 · 5H2O liter
1 either without or with one of the
following N sources:
(NH4)2S2O4 (0.5, 2, or
5 mM), NaNO3 (5, 15, 30, 60, or 120 mM), NaNO2
(0.1, 0.5, 1, 5, 15, 30, 60, or 120 mM), glutamine (0.5, 2, or 5 mM), glutamate (0.5, 2, or 5 mM), urate (0.5, 2, or 5 mM), allantoin (0.5, 2, or 5 mM), and urea (0.5, 2, or 5 mM). Organic N sources in ND medium
were added by sterile filtration following autoclaving, and the pH of
all media was 7.6. Each flask was inoculated with N-starved SH-94-5
cells to a final density of 105 cells ml
1,
and growth was monitored as absorbance at 750 nm
(A750). The turbidity at this wavelength was
found to be linearly related to cell density over the range of values
used in the experiments (A750 < 0.45 [data not shown]).
1. Subsamples (500 µl) of the suspension were spread
plated onto ND plates supplemented with 0.9 mM NaNO3, 0.4 mM Na2S2O3 · 5H2O, and 6.67 mM NaHCO3. A total of 1.3 × 1010 cells were plated. To estimate plating efficiency
on NDA medium, triplicate spread plates of 2 × 104
cells each were made. Plates were incubated as described above and
monitored for colonies over 3 weeks.
1 (19). NDA medium-grown,
mid-exponential-phase cells were harvested by filtration and rinsed
with and resuspended in D medium, which contains nitrate as the sole N
source. After incubation for 5 h under standard maintenance
conditions, cells were concentrated by filtration, rinsed, and
resuspended in double-distilled H2O. Aliquots of cells
containing ~200 µg of protein, as determined with the Sigma
bicinchoninic acid assay (40), were added to the reaction
mixture, incubated for 20 min under maintenance conditions, and assayed
every 5 min for nitrite production using the colorimetric assay of
Snell and Snell (41). Activity was expressed as nanomoles of NO2
produced per minute per milligram of
protein. No activity was ever observed in reaction mixtures which
lacked cells, contained cells boiled for 15 min prior to assaying,
lacked methyl viologen, or lacked sodium dithionite.
removed per minute per milligram of
protein. No detectable activity was observed in extracts boiled for 15 min prior to assaying.
GS assay.
Subcultures of mid-exponential-phase, NDA
medium-grown SH-94-5 cells were rinsed with either NDA medium or N-NDA
medium [NDA without
(NH4)2S2O4] and
subsequently incubated for 48 h under standard maintenance
conditions in that medium (NDA), after which time the
A750 of both subcultures was ~0.25. A portion
(260 ml) of each subculture was filtered, rinsed with 0.3 M phosphate
buffer (pH 7.5) containing 1 mM cysteine, and resuspended in 10 ml of buffer. Crude extracts were produced as described above. The GS activities of five replicate aliquots of cell extracts containing 30 to
50 µg of protein were estimated using transferase assays (7). The assay duration was 20 min, and activity was
expressed as nanomoles of
-glutamyl hydroxamate produced per minute
per milligram of protein.
-Glutamyl hydroxamate production in
control assays containing enzyme extracts boiled for 15 min was less
than 5% of reported GS activities.
DNA isolation, amplification, and sequencing. Genomic DNA was isolated by the method of Pitcher et al. (37). Fragments of the 16S rRNA gene spanning Escherichia coli nucleotide positions 360 to 1335 were amplified in 50-µl reaction mixtures containing 10 mM Tris-HCl (pH 8.3), 50 mM KCl, a 200 µM concentration of each deoxynucleoside triphosphate, 1.12 mM MgCl2, 1.25 U of Taq polymerase (Perkin-Elmer), ~10 ng of genomic DNA, and 0.2 µM (each) primer CYA359F (34) and primer PLG2.3 [5'CTTCA(C/T)G(C/T)AGGCGAGTTGCAGC3'], a modification of PLG2.1 (43). Reaction conditions were 40 cycles of 94°C for 1 min, 58°C for 1 min, and 72°C for 2 min. Amplification products were purified with the QIAquick-spin PCR purification kit (Qiagen), and cleaned amplification products were directly sequenced with an ABI Prism 377 at the University of Oregon's DNA sequencing facility.
Sequence alignment and phylogenetic analyses. Gene sequences were aligned using Malign 2.77 (47) as described by Miller and Castenholz (33). Briefly, this was a pairwise alignment which accounted for secondary structure of the mature 16S rRNA molecule with a gap cost to substitution cost of three.
Phylogenetic trees were constructed according to three optimality criteria. A neighbor-joining tree was built with MEGA (version 1.01; S. Kumar, K. Tamura, and M. Nei, The Pennsylvania State University, University Park). For the calculation of a distance matrix, Kimura's two-parameter model was assumed (24), and nucleotide positions containing gaps or missing data were deleted in a pairwise fashion. The tree was inferred with pairwise deletion of gaps and with 1,000 bootstrap pseudoreplicates. A maximum-parsimony phylogeny was constructed using PAUP (version 3.1.1; D. L. Swofford, Sinauer Associates, Sunderland, Mass.) by a heuristic search using the tree-bisection-reconnection branch-swapping algorithm. Starting trees were obtained by stepwise addition of sequences and 10 replications of random sequence addition. The analysis was bootstrap pseudoreplicated 100 times. A maximum-likelihood tree was created with the "dnaml" program in PHYLIP (version 3.5c; J. Felsenstein, Department of Genetics, University of Washington, Seattle) with a transition-to-transversion ratio of two, sequential addition of sequences, and 100 bootstrap pseudoreplicates. All trees were rooted with Aquifex pyrophilus. The ability of cyanobacterial ancestors (the internodes in the phylogenies described above) to use nitrate was reconstructed for each of the three phylogenies described above according to the maximum-parsimony algorithm of Maddison and Maddison (MacClade, version 3.01; W. P. Maddison and D. R. Maddison, Sinauer Associates, Sunderland, Mass.). This analysis estimated the minimum number of evolutionary steps (i.e., losses of the ability to assimilate nitrate) required to produce the observed distribution of the nitrate assimilation phenotype among extant cyanobacteria. GenBank nucleotide accession numbers for organisms used in phylogenetic analyses are as follows: Aquifex pyrophilus, M83548; E. coli, J01859; Bacillus subtilis, X60646; Synechococcus sp. strain PCC 6307, AF001477; Synechococcus sp. strain PCC 6301, X03538; Leptolyngbya sp. strain PCC 7375, AF132786; Leptolyngbya sp. strain PCC 73110, X84810; Leptolyngbya foveolarum, X84808; Microcoleus sp. strain PCC 7420, X70770; "Mastigocladus" sp. strain PCC 7518, X68780; Cylindrospermum sp. strain PCC 7417, AJ133163; Nostoc sp. strain PCC 7120, X59559; Nostoc sp. strain PCC 73102, AF027655; Prochloron sp., X63141; Pleurocapsa sp. strain PCC 7516, X78681; Synechococcus sp. strain PCC 7002, D88289; Spirulina sp. strain PCC 6313, X75044; Microcystis sp. strain PCC 7941, U40340; Synechocystis sp. strain PCC 6803, D64000; Synechococcus sp. strain C9, L35481 to 83; and Synechococcus sp. strain SH-94-5, AF285260. Sequences for Chamaesiphon sp. strain PCC 7430, Chroococcidiopsis sp. strain PCC 7203, Gloeobacter sp. strain PCC 7421, Myxosarcina sp. strain PCC 7312, and Oscillatoria amphigranulata NZ-Concert-Oa were obtained from Ribosomal Database Project II (http://www.cme.msu.edu/RDP).Nucleotide sequence accession numbers. The 16S rRNA gene sequence data obtained for the strains used in this study have been submitted to GenBank and can be found under the accession numbers AF317503 to AF317510.
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RESULTS |
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Enrichment and isolation. The three media used for the enrichment of the South Harney Hot Spring sample differ both in quality and in quantity of combined N. D medium contains 9.2 mM nitrate but no ammonium, BG11 medium has 5.9 mM nitrate and 25 µM ammonium, and NT medium contains 9.2 mM nitrate and 0.76 mM ammonium. The most successful enrichment was in NT medium, in which a dense, chlorophyll-rich suspension of the unicellular cyanobacterium Synechococcus developed. Small pellets of yellow Synechococcus cells formed in six BG11 enrichments, while no growth was observed in D medium. Transfer of pellets formed in BG11 medium to NT medium resulted in greening of the cells and exponential growth, while transfer of cells from NT medium to either BG11 or D medium led to rapid yellowing of Synechococcus cells (not shown). Based on these observations and the ammonium levels of the respective media, it was suspected that the enriched Synechococcus could not grow on inorganic N sources other than ammonium. An axenic isolate, Synechococcus sp. strain SH-94-5 (CCMEE-5231), was obtained from the NT enrichment for characterization of N sources supporting growth.
N sources supporting SH-94-5 growth.
Consistent with
predictions based on observations from the enrichments, ammonium was
the only inorganic N source tested which supported SH-94-5 growth,
although decreases in the growth rate occurred with increasing
concentrations of
(NH4)2S2O4 (Table
1). SH-94-5 could not grow with either
nitrate or nitrite as the sole N source (Table 1), even at
concentrations great enough for the substrate to be available by
passive diffusion (35, 36). These results suggest that the
failure of SH-94-5 to grow with these N sources is not simply due to
the lack of active transport of these substrates. Cells bleached within
~72 h of exposure to NaNO2 at a concentration of
5 mM.
SH-94-5 also did not grow with N2, indicating that this
clone cannot fix N under aerobic conditions.
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Reversion assay. No revertants capable of growth on nitrate were obtained upon the plating of 1.3 × 1010 N-starved SH-94-5 cells on medium containing 0.9 mM NaNO3. The mean plating efficiency ± the standard error on NDA plates was 16.6% ± 1.62%.
Lack of Nar and Nir activities in SH-94-5.
SH-94-5 cells
lacked both Nar and Nir activities (Table
2). Enzyme activities were assayed after
5 h of preincubation in nitrate-containing medium, conditions
under which Nar and Nir activities would be expected to be maximized
(18, 20). The positive control, Synechococcus
sp. strain C9 (8), previously determined to be the sister
organism of SH-94-5 by phylogenetic analysis (33),
exhibited activity for both enzymes (Table 2).
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Presence of functional NtcA in SH-94-5. The lack of Nar and Nir activities under nitrate-assimilating conditions can result from nonfunctional reductases and/or a nonfunctional regulator of nitrate assimilation. The protein NtcA is required for the transcription of nitrate assimilation genes. It also has a positive effect on the transcription of glnA, which encodes GS (29), and cyanobacteria have higher GS activity in the absence of ammonium as a consequence of NtcA activity (49). However, N-starved and ammonium-replete cells of laboratory mutants of Synechococcus sp. strain PCC 7942 lacking functional NtcA show no difference in GS activity, whereas the wild type exhibits approximately twofold-greater activity under N starvation (44). To determine whether SH-94-5 has functional NtcA, the presence of active protein was assessed indirectly by estimating the GS activities of crude extracts from ammonium-replete and N-starved SH-94-5 cells. The activity of ammonium-replete cell extracts was ~56% of that of N-starved cell extracts (Table 2). The inability of SH-94-5 to assimilate nitrate and nitrite is therefore not due to the loss of NtcA activity.
Distribution and evolutionary origins of nitrate assimilation
deficiencies in cyanobacteria.
In addition to
Synechococcus sp. strain SH-94-5, several other
cyanobacterial isolates representing three genera lack the ability to
grow with nitrate (Table 3). We took a
phylogenetic comparative approach to establish whether this phenotype
had a single origin predating diversification of these organisms or whether it evolved multiple times during the evolutionary history of
the cyanobacteria.
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and
PE
and nitrate+ O. amphigranulata
sequences are 2.8% divergent over the entire fragment.
A neighbor-joining phylogeny indicates that none of the organisms which
are unable to utilize nitrate are closely related (Fig.
1). This phylogeny exhibits many
similarities with both a maximum-likelihood tree and the single most
parsimonious tree obtained using maximum parsimony (not shown).
Synechococcus sp. strain SH-94-5 was found to be the sister
organism of Synechococcus sp. strain C9 in all trees with
strong bootstrap support (Fig. 1) (33). Their sequences
are identical at 99.0% of the nucleotide positions, excluding 27 bp of
missing data in the C9 sequence and six ambiguous nucleotides. These
Synechococcus strains did not group with
Synechococcus sp. strain SH-94-45, a South Harney isolate
identical to group I hot spring Synechococcus
(33) which can grow on nitrate (Table 3). The two sequence
groups of O. amphigranulata clustered together with strong
bootstrap support in all phylogenies (Fig. 1). Similarly, in all three
trees Leptolyngbya sp. strains PCC 9207 and PCC 9221 formed
a clade with Leptolyngbya sp. strain PCC 7375 and
Synechococcus sp. strains PCC 6301 and PCC 6307, while
Geitlerinema sp. strain PCC 9222 was part of a clade
consisting of Chroococcidiopsis sp. strain PCC 7203, Microcoleus sp. strain PCC 7420, and the heterocystous
cyanobacteria, although the topology of this clade varies across trees.
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DISCUSSION |
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A number of lines of evidence indicate that
Synechococcus sp. strain SH-94-5 was derived from a
population of nitrate assimilation-deficient cells comprising a
numerically significant component of the South Harney Hot Spring
microbiota at the time of collection. That these cells were abundant
community members is supported by the enrichment results, since several
enrichments like the one from which SH-94-5 was isolated were obtained
from inocula which had been diluted to a total of 5 cells from a
homogenate with an initial density of ~107 cyanobacterial
cells ml
1. The fact that SH-94-5-like cells came up in
multiple enrichment flasks also makes it likely that cells with this
phenotype were present in the collected sample rather than a product of
mutation in laboratory culture. Results of the reversion assay also
support the conclusion that this phenotype is not a product of recent mutation in the laboratory. The reversion rates of nitrate assimilation mutants of Synechococcus sp. strain PCC 7942 created by
mutagenization with either UV radiation or nitrosoguanidine ranged from
10
7 to 10
9 (44), but we found
no revertants to a nitrate-utilizing phenotype among > 1010 SH-94-5 cells.
SH-94-5 can grow on a number of N sources, with ammonium and glutamine being the best observed substrates for growth (Table 1). The doubling time of ammonium-grown SH-94-5 increased with increasing ammonium concentration over the tested range of 0.5 to 5 mM (Table 1). This pattern may result from the inhibitory effects of high ammonia concentrations on the water-splitting enzyme of photosystem II (21). Like many cyanobacteria, SH-94-5 can grow with urea as the sole N source, but only at rates much lower than those reported for other strains (see references 23 and 25 for examples). SH-94-5 showed slow growth on two intermediates of the purine degradation pathway, urate and allantoin (Table 1). These results differed from those obtained for another nitrate assimilation-deficient cyanobacterium, O. amphigranulata NZ-Concert-Oa, which exhibited higher growth rates with ~1 mM urea, urate, and allantoin than with 4 mM ammonium (E. Jensen and R. W. Castenholz, unpublished data).
The inability of SH-94-5 to grow on either nitrate or nitrite over the
wide range of concentrations tested (Table 1) suggests that the lack of
growth is not simply due to a failure to actively take up these N
sources. A transport mutant of Synechococcus sp. strain PCC
7942 with nrtA interrupted by the insertion of an
aminoglycoside 3'-phosphotransferase gene did not grow in medium
containing 2 mM KNO3, while the wild type doubled about
twice a day at this concentration (36). The growth rate of
this mutant, however, increased with increasing
[NO3
] between ca. 5 and 40 mM, as more
substrate became available for intracellular reduction by passive
diffusion. Additionally, at the pH of the media used in this study,
nitrite is expected to be available (as nitrous acid) by passive
diffusion at concentrations greater than about 100 µM
(35). SH-94-5 exhibited no growth at increasing
concentrations of either N source, which is consistent with the
interpretation that this clone cannot reduce intracellular nitrate or nitrite.
The enzyme assays provided further evidence that SH-94-5 does not have functional Nar or Nir (Table 2). O. amphigranulata NZ-Concert-Oa also lacks activity of these enzymes (Jensen and Castenholz, unpublished). The failure of SH-94-5 to express Nar and Nir is not due to nonfunctional NtcA (Table 2). Like nitrate assimilation genes, ntcA transcription is itself subject to ammonium repression, although weak constitutive transcription has been found for Synechococcus sp. strain PCC 7942 and Anabaena sp. strain PCC 7120 (29, 38). An ntcA mutant of Anabaena sp. strain PCC 7120 exhibits wild-type growth rates on ammonium but appears to have a poorer yield (46). In addition to failing to up-regulate GS activity and ammonium transport during N starvation, ntcA mutants of Synechococcus sp. strain PCC 7942 were estimated to perform worse than the wild type for both of these functions under ammonium-replete conditions (44). The above results suggest that there might be selection to maintain functional NtcA even under conditions of ammonium availability.
It should be considered whether other proteins involved in the regulation of N assimilation may affect the SH-94-5 phenotype. In the presence of nitrite, NtcB, a member of the LysR family of transcription factors, specifically promotes nirA operon transcription in Synechococcus sp. strain PCC 7942 (1). However, since an ntcB deletion mutant of this cyanobacterium can grow with nitrate at ~70% of the wild-type rate (42), it is doubtful that the inability of SH-94-5 to use nitrate is due to the loss of NtcB activity.
PII, an NtcA-regulated phosphoprotein homologous to GlnB in enterobacteria, coordinates carbon and N metabolism in Synechococcus sp. strain PCC 7942 and may exist in one of four phosphorylation states (10, 27). PII is always dephosphorylated in the presence of ammonium and highly phosphorylated during N starvation, whereas the degree of phosphorylation in nitrate-grown cells depends upon factors such as CO2 availability (10, 11). PII does not appear to be involved in the regulation of N assimilation genes during ammonium repression, since the PII null mutant MP2 of Synechococcus sp. strain PCC 7942 displays the wild-type phenotype of increased Nar, Nir, and GS activities after transfer from ammonium- to nitrate-containing medium (11). The authors' observation that MP2 cannot grow in ammonium-containing medium at a pH greater than 8 suggests that a PII null mutant might actually be selected against in some ammonium-containing environments. On the other hand, MP2 is released from wild-type reduction in nitrate assimilation under conditions of nitrate repletion but low CO2 availability (11), and it has been suggested that dephosphorylated PII is involved in the posttranslational negative regulation of nitrate uptake under these conditions. If this is the case, it is expected that a hypothetical mutant with permanently dephosphorylated PII resulting from a nonfunctional kinase would not assimilate nitrate except under passive-diffusion conditions. It is unlikely that SH-94-5 is such a mutant since it cannot grow with a high concentration of nitrate (Table 2).
We conclude that the inability of SH-94-5 to use either nitrate or nitrite is probably due at least in part to mutational inactivation of narB and nirA, which encode Nar and Nir, respectively. However, we presently cannot rule out the possibility that the lack of expression of these enzymes is not simply due to changes in an upstream promoter sequence (or sequences) such that it can no longer be recognized by NtcA, although we would have expected to find detectable rates of reversion to a nitrate-utilizing phenotype for such a regulatory mutant.
Ancestral state reconstruction of discrete characters along a phylogeny is a useful method for estimating the timing of evolutionary events and for testing for shared versus independent origins of phenotypic traits, particularly when transitions between character states are rare (MacClade, version 3.01; Maddison and Maddison), as is the case with our data set. Because nitrate assimilation deficiencies appear to have evolved multiple times in distantly related cyanobacteria from diverse habitats in different geographical locations (Fig. 1; Table 3), we expect that the molecular genetic basis of inactivation of nitrate assimilation has differed in different lineages. Inactivation may have been the result of mutations of different classes (e.g., nonsense mutation versus deletion) at different sites or potentially different loci (e.g., narB versus nirA). Determining the actual mutational event which inactivated nitrate assimilation in a particular lineage, however, would likely be difficult unless it were of very recent evolutionary origin. This is because a gene would be expected to evolve at an accelerated (neutral) rate following inactivation. Nonetheless, we would expect the sequences of inactivated nitrate assimilation genes from different cyanobacteria to exhibit unique molecular signatures reflecting their independent histories of mutation accumulation, a pattern which would corroborate the hypothesis of independent evolutionary origins supported by the phylogenetic distribution of nitrate assimilation deficiencies (Fig. 1).
It is possible that these independent evolutionary events share an
ecological correlate. Since nitrate assimilation is repressed by
ammonium, populations occupying ammonium-replete habitats may exist for
generations under conditions in which mutational inactivation of genes
involved in the assimilation of nitrate and nitrite would not be
deleterious. Synechococcus sp. strain SH-94-5 was isolated from an ammonium-rich hot spring (955 µg liter
1),
(C. E. Wingard, J. R. Schiller, S. R. Miller, and
R. W. Castenholz, unpublished data), while its closest known
relative, Synechococcus sp. strain C9, which grows well on
nitrate, was obtained from Octopus Spring, Yellowstone National Park, a
spring with no detectable ammonium (3). O. amphigranulata (Table 3) is found in New Zealand hot springs with
ammonium levels varying between 200 and 1,200 µg liter
1
(16). Ammonium is continuously supplied to the above
habitats by their respective geothermal sources. The peridunar pond
from which Leptolyngbya sp. strain PCC 9207 (Table 3) was
isolated varied in ammonium concentration from ~10 to 200 µg
liter
1 during a 2-year limnological survey
(28). We were not able to obtain water chemistry data for
the collection sites from which Leptolyngbya sp. strain PCC
9221 and Geitlerinema sp. strain PCC 9222 were isolated
(Table 3). However, all strains for which we have environmental data
were isolated from ammonium-replete habitats, which is consistent with
the hypothesis that nitrate assimilation deficiencies can attain high
frequency or fixation only in populations in which individuals are
released from selection to maintain functional nitrate assimilation
genes by persistent environmental ammonium.
The observation of convergent phenotypes in unrelated organisms with shared ecologies is often considered to be evidence for adaptation (15). It is not clear, however, whether natural selection favored these losses of the ability to assimilate nitrate. Although no transcripts of nitrate assimilation genes can be detected during ammonium repression (9), cell extracts and permeabilized cells of a few cyanobacterial strains do exhibit very low activities of Nar and Nir (18, 20). Expression of these proteins would serve little purpose in vivo under these conditions, however, since ammonium very efficiently inhibits all nitrate and nitrite transport across the cell membrane (19). A mutant which diverted resources ordinarily allocated toward basal expression of the nitrate assimilation machinery toward other purposes might therefore have a selective advantage under ammonium repression. On the other hand, if the loss of nitrate assimilation genes were somehow favored during ammonium repression, we might not expect to find cyanobacteria capable of utilizing more oxidized forms of inorganic N in ammonium-replete habitats. This is not the case, for we have isolated a number of clones from South Harney Hot Spring which grow well with nitrate as the sole N source, including Synechococcus sp. strain SH-94-45 (Table 3; Fig. 1) and a filamentous cyanobacterium (unpublished results). The latter was cloned from an enrichment in D medium of 10 cells/trichome, which indicates that it was derived from an abundant natural population.
Alternatively, these independently derived losses of the ability to use nitrate may be examples of neutral, nonadaptive evolution in which one or more nitrate assimilation genes have degenerated by mutation into pseudogenes over generations of transcriptional repression by environmental ammonium. These neutral alleles could attain high frequency or fixation in a population by drift or, more likely, by being linked to favorable alleles at other loci during episodes of periodic directional selection (2). Evidence for genetic hitchhiking of neutral alleles during such selective sweeps in natural populations of E. coli has been provided by Guttman and Dykhuizen (17). Diversification of ecological requirements, therefore, is not necessarily always adaptive.
Regardless of the evolutionary basis of nitrate assimilation deficiencies in these cyanobacteria, the loss of the ability to utilize nitrate would be deleterious in some environments and consequently could act as a barrier to migration. That is, while the ability of nitrate assimilation-deficient cyanobacteria to disperse between ammonium-containing habitats is suggested by the demonstration of clones with identical 16S rRNA gene sequences from lakes in Europe and South America (Leptolyngbya sp. strains PCC 9207 and PCC 9221), a dispersing nitrate assimilation-deficient cell would not be expected to successfully colonize ammonium-depleted but otherwise suitable habitats. For example, a Synechococcus sp. strain SH-94-5 cell would be expected to starve for N in Octopus Spring, Yellowstone National Park, from which its nitrate-utilizing sister, Synechococcus sp. strain C9, was isolated. The derivation of nitrate assimilation-deficient cyanobacteria in ammonium-replete habitats therefore may illustrate how ecology and evolution can interact to shape biogeography in the microbial world.
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ACKNOWLEDGMENTS |
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We thank Carrie Inman for her helpful assistance and two anonymous reviewers for their comments and suggestions.
This work was supported by U.S. National Science Foundation grants IBN-9219273 and IBN-9630674 to R.W.C. and by an NSF research training grant (DBI-9413223) to the Department of Biology at the University of Oregon.
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FOOTNOTES |
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* Corresponding author. Present address: Mailstop 239-4, NASA Ames Research Center, Moffett Field, CA 94035. Phone: (650) 604-6052. Fax: (650) 604-1088. E-mail: srmiller{at}mail.arc.nasa.gov.
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