doi:10.1111/j.1420-9101.2009.01691.x
Lacustrine radiations in African Synodontis catfish
J. J. DAY,*,
R. BILLSà & J. P. FRIEL§
*Department of Genetics, Evolution and Environment, University College London, London, UK
Department of Zoology, The Natural History Museum, Cromwell Road, London, UK
àSouth African Institute for Aquatic Biodiversity, Grahamstown, South Africa
§Cornell University Museum of Vertebrates, Ithaca, NY, USA
Keywords:
Abstract
brood parasitism;
cichlid fishes;
lacustrine diversification;
Lake palaeo-Makgadikgadi;
Lake Tanganyika;
molecular dating.
Synodontis catfish are a species-rich, tropical pan-African genus that predominately occur in fluviatile environments, but which also form a small radiation
within Lake Tanganyika (LT). Here we estimate Synodontis relationships, based
on mitochondrial and nuclear DNA, greatly expanding previous sampling.
Data were analysed using different methods of phylogenetic inference:
Bayesian (also testing compositional heterogeneity), likelihood and parsimony, in order to investigate biogeographic history and the extent of
intralacustrine speciation within this group. Bayesian-relaxed clock analyses
were used to estimate timings of radiations. Our analyses reveal a single origin
of the LT flock with the inclusion of the nonendemic S. victoriae, and that these
taxa evolved relatively recently (5.5 Ma), considerably later than the formation of LT (9–12 Ma). Two internal endemic clades diversified at a similar time
(2–2.5 Ma), corresponding to a period of climate change, when lake levels
dropped. We find evidence for a further species flock, composed of riverine
southern African taxa, the diversification of which is very rapid, 0.8 Ma (95%
HPD: 0.4–1.5) and infer a similar scenario for the diversification of this flock to
southern African serrachromine cichlids in that they radiated in the now
extinct lake Makgadikgadi. We also reveal that the biogeographic history of
Synodontis catfish is more complex than previously thought, with nonmonophyletic geographic species groupings.
Introduction
Lakes, analogous to islands, are notable in presenting
settings conducive for evolutionary radiations (Turner,
1999) and thus offer fruitful systems in which to study
processes that generate biodiversity. In particular, the
lakes of the East African rift have received considerable
attention due to the diverse endemic faunal radiations,
most pronounced in cichlid fishes (Fryer & Iles, 1972).
Radiations of noncichlid faunas are reported from
ancient lake settings (lakes > 100 000 years), with the
highest levels of diversity and endemicity occurring in
the oldest of the great lakes, Lake Tanganyika (LT, 9–
Correspondence: Julia J. Day, Department of Genetics, Evolution and
Environment, University College London, Gower Street, London WC1E
6BT, UK.
Tel.: +44 2076792660; fax: +44 2076797096; e-mail: j.day@ucl.ac.uk
12 Myr, Cohen et al., 1993). Here, numerous unrelated
species flocks occur including catfish, spiny-eels, gastropods, crabs and ostracods, for example (Coulter, 1991).
Cichlids and gastropods aside, these radiations are on a
much smaller scale (10–15 species) and at a lower
taxonomic rank. Until recently (West & Michel, 2000;
Wilson et al., 2004; Day & Wilkinson, 2006; Koblemüller
et al., 2006; Marijnissen et al., 2006, 2008) the evolutionary significance of such faunas has been overlooked;
yet, they provide important comparative systems that
may help us to better understand processes responsible
for clade diversification and generalities across diverse
taxa.
Synodontis catfish (Siluriformes: Mochokidae) are one
of the most species-rich African fish genera (120
species, Poll, 1971). High species richness and their subSaharan distribution similar to that of cichlids make them
a useful comparative system. However, relatively little is
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J. J. DAY ET AL.
known about their evolutionary history, although two
recent studies have begun to address this, focussing on
their radiation within LT (Day & Wilkinson, 2006;
Koblemüller et al., 2006). This species flock comprises
10 endemic, largely cryptic species (Wright & Page, 2006)
as well as the nonendemic S. victoriae (Day & Wilkinson,
2006). Independent molecular studies of this radiation
(Day & Wilkinson, 2006; Koblemüller et al., 2006) aimed
to test the monophyly, and their colonization history of
LT. These studies, including similar taxonomic sampling,
but utilizing different mitochondrial (mt)DNA markers
(entire cytochrome b, Day & Wilkinson, 2006; partial
ND6 and partial control region, Koblemüller et al., 2006),
found conflicting results regarding the evolutionary
relationships of the LT flock, and because of differences
in calibrations, subsequent interpretation of the colonization of LT. Although both studies support a nonmonophyletic endemic flock, a finding that mirrors LT cichlid
fish evolution (Salzburger et al., 2002), this is a consequence of differences in putative relationships between
nonendemic taxa (Fig. 1). Koblemüller et al. (2006)
interpret the overall lack of phylogenetic signal between
the six East African lineages as evidence of relatively
rapid speciation. Conversely, regardless of phylogenetic
analysis, Day & Wilkinson (2006) recover two wellresolved East African clades, one of which comprises all
Tanganyika endemics and the inclusion of the nonendemic S. victoriae from Lake Victoria. These authors
estimate a divergence time for the LT flock (including
S. victoriae) to post-date the origin of LT, largely coinciding with the onset of full lacustrine conditions, which
occurred approximately 5–6 Ma (Cohen et al., 1997),
with individual endemic clades (Fig. 1a and b) diversifying relatively recently (< 3 Myr), as has also been
(a)
Outgroups
(b)
S. nigromaculata
*
reported in LT crabs (Marijnissen et al., 2006). This is a
very different scenario from that of Koblemüller et al.
(2006), whose estimated dates for these clades are
considerably older at 12 and 6–7.8 Myr, respectively,
with the implication that the former clade diversified in
nonlacustrine conditions. As ultimately we may wish to
incorporate these data into a broader picture investigating evolutionary processes within this environment, it is
important to qualify these results and test alternate
hypotheses concerning their evolution.
In contrast to cichlid fishes, the majority of Synodontis
diversity is within fluviatile habitats, reaching a maximum in central Africa, principally the Congo drainage
basin (Poll, 1971). However, it has recently been shown
that past environments have played an important role on
current cichlid diversity. Genetic evidence reveals that
current diversity of riverine cichlids in southern Africa is
the product of adaptive radiation in a now extinct lake
basin (Joyce et al., 2006). That Synodontis have radiated
within LT suggests they may be more prone to lacustrine
diversification. In the light of cichlid research, it is
possible that this mechanism may also be invoked to
account for the present genetic diversity of southern
African species. It is unknown whether southern Africa
taxa (nine described species, Skeleton, 2001) form a
monophyletic grouping, or not, and although initial
studies infer a close relationship between the southern
species S. nigromaculata and S. zambezensis, and those from
Lakes Tanganyika and Malawi (Day & Wilkinson, 2006;
Koblemüller et al., 2006), this has not been thoroughly
tested. To test this hypothesis and re-examine the origins
of the LT species flock, we present a molecular phylogeny
based on both mtDNA and nuclear (nc)DNA of Synodontis
catfish, greatly expanding taxonomic sampling of previous studies. All geographic areas are included with
multiple species, so that we are also able to test their
monophyly and the importance of past vicariance events.
Methods
S. njassae
Taxon selection and DNA methods
S. granulosa
i
*
*
S. multipunctata
*
S. lucipinnis
*
*
ii
S. polli
**
*
S. irsacae
*
S. petricola
S. victoriae
Fig. 1 Consensus based on taxa common to the studies of (a) Day &
Wilkinson (2006) and (b) Koblemüller et al. (2006). Support values
(Bayesian posterior probabilities) indicated by *(> 95%),
**(90–95%). Taxon names for LT endemic species are revised
following Wright & Page (2006) and are highlighted in bold.
A total of 65 Synodontis samples representing 40 species
(33% of known species diversity) and two outgroup taxa
(mochokids) are included in the phylogenetic analyses
(Appendix 1). Taxa were sampled from the majority of
major African drainage basins, with particular emphasis
on East and southern species. All LT species are included
with the exception of S. dhonti (only one specimen
known, Wright & Page, 2006) and the nonendemic
S. melanostrictus (Wright & Page, 2006). The southern
African species, S. macrostoma, is omitted from this study
due to the degraded nature of DNA from our only
sample.
Genomic DNA was extracted from white tissue and fin
clips using DNA purification kit (Qiagen Ltd, UK). As
mtDNA and ncDNA are inherited in different ways, we
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Lacustrine radiations in African Synodontis catfish
targeted genetic markers from each genome, in order to
independently validate our phylogenetic hypothesis. Cytochrome b (mtDNA) provided good resolution in a
previous study of LT Synodontis (Day & Wilkinson,
2006). Although ncDNA is more slowly evolving, the
ribosomal protein-coding gene S7 (rpS7) has proved
useful in studies of relatively young faunas at a comparable taxonomic level (e.g. Feulner et al., 2006; Schelly
et al., 2006). Published primers were used to amplify
cytochrome b and tRNA (Hardman & Page, 2003;
Hardman, 2005) using varied primer annealing temperatures (49–55 C). rpS7 (Chow & Hazama, 1998) was
amplified (826 bp in Synodontis), with a primer annealing temperature of 55 C, with only the first intron
sequenced (530 bp). Samples were analysed using an
ABI 3730xl sequencer (Applied Biosystems, UK). All
sequences are deposited in GenBank. We further use
published mtDNA sequence data (Day & Wilkinson,
2006; Koblemüller et al., 2006). See Appendices 1 and 2
for all GenBank accession numbers.
807
software (p4). Branch support was evaluated using
Bayesian posterior probabilities (MR BA Y E S and p4) and
ML nonparametric bootstrapping (1000 pseudoreplicates,
G A R L I ). Further Bayesian (MR BA Y E S ) and ML analyses,
were performed on single gene sets (65 samples mtDNA;
54 samples ncDNA) to determine taxon validity (mtDNA)
and congruence of data sets. The same settings were
employed as before and the models closest to the optimal
models, GTR + I + G (mtDNA data) and HKY + G
(ncDNA data), selected in M O D E L T E S T implemented.
Finally, a subset of taxa (13 species, see Appendix 2)
common to the data sets of Day & Wilkinson (2006) and
Koblemüller et al. (2006), incorporating all genetic data:
mtDNA (cytochrome b + tRNA, partial ND6, partial
D-Loop) and ncDNA (rpS7 intron 1, this study), was
subsequently analysed using ML and maximum parsimony (M P , P A U P * Swofford, 2002) to test alternative
hypotheses regarding the evolution of the LT radiation
(Fig. 1) and evaluate the strength of phylogenetic signal.
Divergence time estimation
Sequence alignment and phylogenetic analyses
Presumed orthologous DNA sequences were aligned in
CL U S T A L X (Thompson et al., 1997) using default parameters and checked manually. Data were analysed using
maximum likelihood (ML), implemented in G A R L I
(Zwickl, 2006) and Bayesian Markov Chain Monte Carlo
(MCMC) analyses were conducted using the programmes
MR BA Y E S v3.1.2 (Huelsenbeck & Ronquist, 2001) and p4
v0.84. r158 (Foster, 2004). The latter programme has the
advantage of assessing compositional heterogeneity
across data sets (Foster, 2004), as well as employing the
polytomy proposal (Lewis et al., 2005). Optimal model
and parameter values were obtained using M O D E L T E S T
v3.7 (Posada & Crandall, 1998). All methods were
performed for the combined data set (54 taxa) as follows:
ML analyses were performed both by estimating parameters and by specifying the optimal model and parameter
values (TVM + I + G) based on the AIC criteria. The
model GTR + I + G was implemented for both Bayesian
programmes as the model closest to that selected using
M O D E L T E S T . MR BA Y E S analyses were run for 2 000 000
generations (four chains, 0.2 temperature) partitioning
these data based on individual genes as well as an
additional analysis also enabling the third codon a
partition-specific model. Optimal composition analyses
were performed using p4 and run for 1 500 000 generations (four chains, 0.05 temperature), with inclusion of
a strong prior for polytomies (i.e. C = log(10)). Composition chi-squared test using predictive posterior simulations conducted in p4, revealed homogeneity of the
ncDNA data, but significant heterogeneity of the mtDNA
data. For the mtDNA data to be regarded as homogenous
(P = 0.99), it was necessary to apply two composition
vectors. Convergence of the MCMC to a stationary phase
was determined using TR A C E R (MR BA Y E S ) and G N U
Timing of speciation events were estimated using Bayesian-relaxed clock methods as the assumption of a
molecular clock was rejected after comparison of likelihood scores for clock and nonclock ML trees using a
likelihood ratio test (LR = 132.30, d.f. = 54, P > 0.05).
We used the programme B E A S T v1.4.6 (Drummond &
Rambaut, 2007), selecting an uncorrelated log-normalrelaxed clock rate variation model and a Yule speciation
tree prior (Drummond et al., 2006), which assumes a
constant rate of speciation per lineage. We selected a
similar model to that implemented in MR BA Y E S for the
combined data set (GTR + I + G), partitioning loci and
codons (first + second vs. third). Different tree priors
(exponential and uniform) were implemented to determine if these would greatly affect subsequent results of
divergence dates. For each tree prior, two independent
MCMC analyses were run, starting from randomly
chosen trees, for 1 000 000 generations, to ensure
individual runs had converged and determine burn-in
(25%). We report results implementing a uniform
prior, as analyses were largely congruent.
We calibrate the ingroup using the oldest occurrence of
Synodontis. Fossils assigned to this genus date from the
Early Miocene (Burdigalian) of Egypt (Priem, 1920) and
Kenya (Greenwood, 1951), although the Egyptian site
(Wadi Moghara) is marginally older, dated at c.18–17 Myr
(Miller, 1999). Although it is considered better practice to
use more than one calibration (Benton & Donghue,
2007), fossil Synodontis cannot reliably be assigned to
extant species (Pinton et al., 2006), despite them being
not uncommon in the fossil record (Stewart, 2001).
Furthermore, use of geographical dates, such as the
maximum ages of the great lakes, is not an independent
means of calibration (McCune, 1997), particularly as
we wish to estimate age of colonization of lacustrine
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environments. To make allowances for the imprecision of
fossil dating, the ingroup (i.e. Synodontis) is calibrated
using the maximum and minimum dates for the Burdigalian period (16.3–21.5 Myr).
Results
Phylogenetic analysis
The combined data matrix consists of 1697 sites. A total
of 1660 bp (cytochrome b, 1058 bp; tRNA 65 bp; rpS7
intron 1, 538 bp) were sequenced for all species, whereas
only cytochrome b + tRNA was sequenced for multiple
individuals in order to test species validity. The alignment
of rpS7 intron 1 included up to 37 indels (up to 22 indels
discounting S. gambiensis). Data were missing for rpS7
intron 1 for S. katangae and S. nigromaculata (CU 91094).
Cytochrome b, contains the most parsimony informative
(PI) sites (175), whereas rpS7 intron 1 (538 bp) has
20 ⁄ 32 PI sites (gaps coded as missing data ⁄ 5th state). The
matrix for a subset of taxa (13 species, Appendix 2)
common to the data sets of Day & Wilkinson (2006) and
Koblemüller et al. (2006) consists of 2530 bp (cytochrome b + tRNA, rpS7 intron 1, partial ND6 and partial
control region). PI sites for ND6 (426 bp) include 46 sites,
with the control region (407 bp) containing 128 ⁄ 387
sites (gaps coded as missing data ⁄ 5th state).
Trees obtained under BI (MR BA Y E S ) and ML methods
are highly congruent (Fig. 2a), with minimal differences
in relationships. Both methods consistently recover two
main clades (A and B, BPP > 75 to < 85; BS 55) and
several internal clades (C–K), which are well supported,
with the exception of clade H. The BI (p4) tree obtained
under a compositional heterogeneity model (Fig. 2b)
differs in that clade B is not recovered. Instead, clades D
and C are recovered as successive sister groups to clade A,
with clade E, plus (S. contractus, S. nigriventris), as sister to
these, although support for this set of relationships is not
strong.
Evaluation of alternative phylogenetic trees using the
approximately unbiased (AU) test (Shimodaira, 2002),
implemented in the programme C O N S E L (Shimodaira &
Hasegawa, 2001), found no tree as significantly worse
fit to the data (P = 0.51–0.49). BI (MR BA Y E S ) trees
based on different data sets (single gene: cytochrome b,
rpS7, combined) were also evaluated using the AU test,
with the tree constructed from cytochrome b data
rejected as significantly worse fit (P > 0.05). There are
several differences in taxon ⁄ clade placements between
this tree and those generated from the rpS7 and
combined data set. These include the placement of
S. gambiensis and S. clarias, recovered as basal members
of clade A and B, respectively, and the alternate
placements of clade C and the clade (S. contractus,
S. nigriventris) within clade B. The instability of
S. gambiensis and S. clarias may be caused by the long
branches of these particular taxa.
Clade A, is composed of two subclades (H and I), the
former and its constituent clades (J and K) are well
supported, as largely are the internal nodes. Support for
the latter (H) is less convincing, although this can be
attributed to the placement of S. gambiensis and S. clarias.
There is strong internal support within clade H for the
placement of the West African S. thysi, with East
African ⁄ Nilotic members (S. frontosus, S. serratus) and a
species (S. af. punctulatus) assumed to have been collected
from Tanzania. The LT endemics, plus the nonendemic
S. victoriae are recovered as a single clade (K, Fig. 2).
Clade J, which includes the Lake Malawi endemic
(S. njassae), is otherwise composed of riverine species
from the Zambezi and Okavango drainage basins (including the widespread S. nigromaculata species complex).
Inclusion of the majority of all described southern
African species reveals a polyphyletic assemblage (Fig. 2),
the placements of which occur in both of the main clades
(A and B). However, the majority of species form a
monophyletic grouping (F), with maximum support (100
BS ⁄ 100 BPP) under all analyses and are most closely
related to the Congolese taxa, within clade B. The
remaining southern African taxa (e.g. S. nigromaculata
species complex and S. zambezensis) occur within clade A
as previously discussed.
Discussion
Increased taxonomic sampling (50% more than previous studies) and additional data, including the first
inclusion of ncDNA, provide an improved estimate of
phylogenetic relationships within Synodontis. Although
sampling is far from complete, the results of this study are
decisive regarding alternate evolutionary hypotheses of
the LT radiation. Furthermore, this study identifies a
novel southern African radiation, which irrespective of
actual dates, reveal a more rapid diversification of this
grouping than the LT radiation. More broadly, the
phylogeny highlights the nonmonophyletic nature of
geographic regions, and thus a considerably more complex history of Synodontis evolution.
Lake Tanganyika radiation revisited
Irrespective of analyses of the combined data set, the LT
endemics, plus the nonendemic S. victoriae are recovered
as a single clade (K, Fig. 2) supporting the hypothesis of
Day & Wilkinson (2006) over that of Koblemüller et al.
(2006). One notable difference in our analyses, although
weakly supported, is that the tree recovered using
compositional heterogeneity places S. victoriae as basal
to all LT endemics (Fig. 2b), rather than internally within
the LT endemic radiation (Fig. 2a). Support for a monophyletic LT endemic clade, plus S. victoriae is largely due
to the stronger signal of the cytochrome b data, as
separate gene analysis reveals inconclusive evidence
from ncDNA data to support this grouping. Although
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Lacustrine radiations in African Synodontis catfish
(a)
100
1.00
100
1.00
94
0.51
98
1.00
100
F
1.00
1.00
53
0.67
64
E
0.55
55
B 0.83
G
1.00
100
98
1.00
C
1.00
0.54
100
D
0.91
100
1.00
91
1.00
82
0.84
100
1.00
56
H
0.88
0.58
86
100
0.99
1.00
84
*
*
*
98
0.98
S. soloni
S. angilica
S. congica
S. pleurops
**
S. greshoffi
S. unicolor
S. af.afrofisheri RM
S. afrofischeri LV
S. afrofischeri LA
S. nigrita
S. rebeli
S. waterloti 1
S. waterloti 2
S. frontosa 1
S. frontosa 2
S. frontosa 3
100
1.00
55
A
57
0.63
0.76
73
0.99
1.00
J
100
1.00
I
1.00
K
ii
71
0.87
1.00
100
1.00
91
1.00
83
0.99
100
1.00
100
i
88
100
87
0.77
71
0.66
84
0.96
*
*
S. zambezensis
S. sp. nov.
S. njassae
S. nigromaculata 1
S. nigromaculata 2
S. nigromaculata 3
S. nigromaculata 4
S. granulosa
S. multipunctata
S. grandiops
S. lucipinnis
S. af.tanganaicae
S. irsacae
S. polli
S. af.ilebrevis
S. petricola
S. victoriae
*
*
*
*
*
**
*
*
*
*
*
S. af.punctulata
1.00
79
0.96
(b)
Microsynodontis sp.
S. contracta
S. nigriventris
S. decora
S. brichardi
S. katangae 1
S. katangae 2
S. woosnami
S. macrostiga
S. leopardina
S. nebulosa
S. af.thamalakanensis
S. vanderwaali
S. clarias
S. gambiensis
S. thysi
S. serrata 1
S. serrata 2
809
*
*
*
*
**
*
**
**
*
*
*
**
**
0.01 changes
Fig. 2 Phylogenetic hypotheses of Synodontis relationships inferred from mtDNA (cytochrome b + tRNA) and ncDNA (rpS7 intron 1).
(a) Consensus of maximum likelihood tree and Bayesian (MR BA Y E S ) consensus. Support values above 50% are shown for bootstrap (above
branches) and Bayesian posterior probabilities (below branches). (b) Bayesian consensus based on P4 analysis employing compositional
heterogeneity model and a strong polytomy prior. Support values > 81 indicated by **(81–90), *(91–100). Southern African species are
highlighted by grey taxon names.
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rpS7 intron 1 and 2 have been shown to be useful for
resolving species-level relationships (e.g. Schelly et al.,
2006), it is probable that this marker is too slowly
evolving and therefore less informative in resolving
relationships for such a young radiation (see below).
Analysis of a subset of taxa (13 species, Appendix 2)
common to the data sets of Day & Wilkinson (2006) and
Koblemüller et al. (2006), incorporating all genetic data
(2530 bp), again strongly supports the inclusion of
S. victoriae within the LT endemic clade (as depicted in
Fig. 1a), with the clade (S. njassae, S. nigromaculata) as
sister. Separate gene analysis of cytochrome b + tRNA
and also ncDNA support this grouping. By contrast,
analysis of partial ND6 does not support this grouping,
although support for alternate relationships is weak.
Analysis of partial control region data finds no resolution
between this set of taxa.
Divergence dates in this study are similar to Day &
Wilkinson (2006), despite the implementation of different dating methods. The endemic LT flock, plus S. victoriae
is estimated to have diverged at 5.5 Myr (95% HPD,
highest posterior distribution: 4.0–7.3), whereas LT
endemic clades i and ii are dated at 3.0 Myr (95% HPD:
1.9–4.4) and 2.5 Myr (95% HPD: 1.6–3.5) respectively
(Fig. 3). In contrast to Koblemüller et al.’s (2006) estimates for these endemic clades (11.2–14.8 and 5–8 Myr
respectively), the dates generated here are relatively
young, being similar to those estimated for the platythelphusid crab radiation (Marijnissen et al., 2006) and
similarly implying rapid diversification of endemic species in situ. LT has had a complex geological and climatic
history, with researchers linking these episodes to speciation events (e.g. Sturmbauer et al., 2001; Day et al.,
2008). As previously proposed (Day & Wilkinson, 2006),
the inferred timing of the Synodontis radiation corresponds to the deepening of LT at around 5–6 Myr (Cohen
et al., 1997), with the two endemic clades diversifying
during a time when LT experienced lower lake levels
through climate change (Cane & Molnar, 2001).
Recently, two timescales have been suggested for
cichlid evolution based on fossil and Gondwanan
break-up calibrations (Genner et al., 2007), leading to
disparate age estimates for the divergence of the LT
cichlid flock at 12 and 18 Myr, respectively. It is therefore
of interest that the evolution of the LT Synodontis catfish
flock is comparable with the younger timescale, with
divergences of all the major cichlid tribes estimated to
have occurred between 6.6 and 3.1 Ma (Day et al., 2008).
It would appear that during this time frame, when a fully
formed LT was subjected to lake-level fluctuations, a
number of groups including catfish and crabs were
diversifying, possibly in response to environmental factors (Day & Wilkinson, 2006; Marijnissen et al., 2006). In
the context of adaptive radiation theory (Schluter, 2000),
it is noteworthy that although LT Synodontis exhibit
recent divergence, this clade displays little morphological
disparity. In contrast to the phenotypically diverse cichlid
fish (e.g. lamprologine cichlids, Day et al., 2007) and
Platythelphusa crab radiations (Marijnissen et al., 2006),
they are instead largely cryptic, and display no sexual
dimorphism. Ecological niche segregation has been
demonstrated to play an important role in the divergence
of crabs (Marijnissen et al., 2008) and cichlids (e.g. Hori,
1991), but has not yet been investigated in Synodontis.
Although the placement of S. victoriae is less robust
(also see Day & Wilkinson, 2006), it appears reasonable,
judging on additional data, that this taxon nests within
the LT radiation. Considering that this species principally occurs in Lake Victoria, which is considerably
younger than the age of this species, dated at 4.4 Myr
(95% HPD: 3.0–6.0), it is plausible to infer that
S. victoriae evolved within the LT basin and has subsequently emigrated. The alternate hypothesis that the
two endemic clades are independent radiations would
imply that the ancestor of these clades made it to LT
during a dry period in this region’s history (Cane &
Molnar, 2001), when presumably aquatic environments
would have shrunk, making mobility for aquatic taxa
less probable. It is likely that the nonendemic LT taxa, S.
melanosticta, is closely related to S. nigromaculata being
closely allied with this species on morphological
grounds (Wright & Page, 2006), and therefore it is
reasonable to infer that it invaded the lake independently to the LT endemics.
Differences in dating between studies appear to be
calibration specific, as opposed to being methodological.
In particular, rather than dating the ingroup using the
oldest fossil, Koblemüller et al. (2006) calibrate their East
African clade using the oldest fossil from that region
(Kenya). Although this ignores a similarly aged fossil
from a non-East African locality (Priem, 1920), it also
assumes a monophyletic East African clade. However, on
the basis of their limited sampling this is not an
assumption that is supported by the current analysis.
Moreover, dating of lacustrine endemics using maximum
lake ages by these authors does not enable independent
means of estimating their divergence, although these
internal calibrations did not appear to impact on estimates, with similar dates obtained when these calibrations are excluded.
Koblemüller et al. (2006) attribute lack of phylogenetic
signal between ‘East African’ lineages (clade I) to rapid
speciation and compare this clade with other examples of
this phenomenon (e.g. Joyce et al., 2005). However,
artefactual causes, indicative of a soft polytomy, should
first be eliminated (Maddison, 1989) before concluding
this scenario. One of the principal causes for the lack of
resolution is insufficient data (characters and taxon
sampling), although other factors, such as data evolving
appropriately for the question, can also be problematic
(Poe & Chubb, 2004). Our results reveal that there is little
evidence for a ‘rapid’ speciation event and that the lack of
phylogenetic signal reported by Koblemüller et al. (2006)
is in this case a result of lack of data. The lack of resolution
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Lacustrine radiations in African Synodontis catfish
811
Microsynodontis sp.
S. rebeli
S. waterloti
S. nigrita
S. soloni
S. congica
S. angilica
S. pleurops
S. af.thamalakalensis
S. nebulosa
S. vanderwaali
S. leopardina
S. woosnami
S. macrostiga
S. decora
S. brichardi
S. katangae
S. contracta
S. nigriventris
S. af.afrofischeri
S. afrofischeri
S. unicolor
S. greshoffi
S. thysi
S. serrata
S. af.punctata
S. frontosa
S. clarias
S. gambiensis
S. nigromaculata 1
S. nigromaculata 2
S. nigromaculata 3
S. sp. nov.
S. njassae
S. zambezensis
S. grandiops
S. multipunctata
S. granulosa
S. af.ilebrevis
S. petricola
S. polli
S. irsacae
S. lucipinnis
S. af.tanganaicae
S. victoriae
Fig. 3 Chronogram inferred from Bayesian dating analysis (B E A S T ) of the combined data set. Node bars indicate 95% posterior distributions.
Grey boxes indicate lacustrine radiations. Light grey: East African taxa; Mid-grey: southern African taxa; Dark grey: central and West African
taxa. Time in Myr.
from the control region regarding the deeper splits
between the main lineages within clade F is unsurprising,
considering the age of this clade, 8.0 Myr (95% HPD: 6.0–
10.4) as the mtDNA control region is rapidly evolving.
Brood parasitism
Among LT species, S. multipunctata has been shown to be
a brood parasite of mouthbrooding cichlids from the tribe
ª 2009 THE AUTHORS. J. EVOL. BIOL. 22 (2009) 805–817
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J. J. DAY ET AL.
Tropheini (Sato, 1986), the first time this behaviour has
been recorded in a nonavian vertebrate group. The
catfish eggs incubated in the cichlid mouths along with
those of the hosts, hatch earlier, and subsequently feed
on their host’s eggs. The extent of brood parasitism in LT
species is unknown, however, although not substantiated in the scientific literature or reported in the wild, S.
petricola and its ‘dwarf form’ (S. lucipinnis, Wright & Page,
2006) also exhibit this behaviour in aquarium conditions
(aquarium web blogs). We might also presume that the
newly described S. grandiops (Wright & Page, 2006) is also
a brood parasite. This species (if indeed distinct) is very
similar to S. multipunctata in terms of morphology and
genetics, with specimens previously catalogued together
under the name, S. multipunctata. Although speculative, it
appears that brood parasitism could have evolved independently in the two endemic LT lineages. Notably,
brood parasitism has a dual origin in old world cuckoos
(Aragón et al., 1999).
Koblemüller et al. (2006) suggest that S. multipunctata
diverged at around the same time as their hosts. However, their estimated date of 2.37 Ma is erroneous, being
the time of origin between the particular population(s) of
this species that they sampled. The correct age of origin of
this species (judging from their timescale) is the time it
diverged from its sister species, S. granulosa, which in
their analysis is 12.0 Ma. However, our date estimates
for both endemic clades (see previous section) do
correspond to newly estimated dates for the Tropheini
3.4 Ma (95% HPD: 2.7–4.5, Day et al., 2008) assuming
the younger calibration for the LT cichlid radiation and
therefore Koblemüller et al.’s hypothesis is thus supported by our analysis.
Evidence for a southern African species flock
Despite the nonmonophyly of the southern African
species (Fig. 1), the majority form a species flock (clade
F), which has evolved from Congolese ancestors. The
recovery of clade F agrees with the preliminary analysis
of partial cytochrome b and allozyme data (Bruwer et al.,
2000), although the monophyly (with the inclusion of
S. macrostoma) was evaluated against only several species,
which include S. nigromaculata, S. njassae, S. petricola and
S. zambezensis in their study. The most notable observation of clade F is that the internal branches are
exceptionally short (Figs 2b and 3), suggesting rapid
cladogenesis. The age of this clade is estimated at
0.89 Myr (95% HPD: 0.42–1.4), and irrespective of
calibration (Loader et al., 2007), it is considerably younger than the LT radiation. Identification of many of these
species is notoriously difficult (J.J. Day & R. Bills,
personal observation) despite field keys (e.g. Skeleton,
2001). Thus, the young age of these species might
explain why morphological characters are not yet totally
fixed and seemingly labile. As Synodontis have been
shown to hybridize in laboratory conditions (S. zambez-
ensis · S. nigromaculata, Bruwer & van der Bank, 2002), it
is therefore possible that there is ongoing hybridization,
particularly as this is a very young species flock (Seehausen, 2004).
It has been proposed that extant southern African
riverine serranochromine cichlids are the result of an
adaptive radiation in a now extinct palaeo-lake, Makgadikgadi (Joyce et al., 2005). This lake, one of Africa’s
largest water bodies (120 000 km2), began to form in the
Pleistocene (315 000–460 000 years), drying up in the
last few thousands years, and would have been located in
Okavango delta region (Moore & Larkin, 2001). Irrespective of calibrations used, the cichlid radiation falls
within this time frame (Genner et al., 2007), and
although the estimated age for the Synodontis species
flock is older, it also falls within the bounds of the upper
confidence limit. As such, it possible that the flock arose
within lacustrine conditions, or at least in conditions
associated with the evolution of this hydrological feature.
Members of the flock subsequently spreading through
southern African rivers, in a similar scenario as hypothesized for the cichlids. Unlike these cichlids, members of
the Synodontis flock have not spread out across Africa to
the same degree, with the majority of species occurring
sympatrically in the Upper Zambezi, Okavango, Kafue
and Cunene river systems, whereas S. nebulosus occurs in
the Middle and Lower Zambezi and Buzi systems (Skeleton, 2001). Although recent evidence from African
weakly electric fish (mormyrids) reveals that adaptive
radiation may proceed in rivers (Feulner et al., 2006), it
seems less likely that the Synodontis species flock could
have arisen in fluviatile conditions considering that we
find no evidence for such rapid diversification in other
river systems (e.g. Congo or Nile) for this group.
In the light of a probable flock that evolved in a now
extinct lake basin, it is of interest that there are no
Synodontis species flocks in either Lakes Malawi or
Victoria. The environment of Lake Victoria is similar to
Palaeolake Makgadikgadi, being a large shallow young
lake, estimated to have formed approximately
400 000 years ago (Johnson et al., 1996), with a probable
complete desiccation period in the late Pleistocene
and subsequent refilling 12 400 years ago. It contains
two unrelated nonendemic species (S. afrofischeri and
S. victoriae). Conversely, Lake Malawi, dated at 8.6 Myr,
with deep water conditions attained 4.5 Ma (Ebinger
et al., 1993; Delvaux, 1995) is a rift environment similar
to that of LT. Cichlids and gastropods aside, it is therefore
somewhat surprising that LM lacks the multiple species
flocks associated with LT, with a single described endemic
species (S. njassae), possibly two (Snoeks, 2004). This
could be as a consequence of environmental factors, in
that LM experienced periodical desiccations estimated to
have occurred as recently as 570 000 years ago (Delvaux,
1995). However, if Synodontis can radiate within this time
frame, then their absence in LM may be due to lack of
available niche space, possibly because of cichlid fishes. It
ª 2009 THE AUTHORS. J. EVOL. BIOL. 22 (2009) 805–817
JOURNAL COMPILATION ª 2009 EUROPEAN SOCIETY FOR EVOLUTIONARY BIOLOGY
Lacustrine radiations in African Synodontis catfish
is notable that although all three great lakes have sizable
cichlid radiations, LT is by far the smaller flock with less
than half the species estimated for LM and LV, yet it
contains greater overall biodiversity.
Synodontis biogeography
Day & Wilkinson (2006) found good support for the
existence of an eastern ⁄ central African split in Synodontis
faunas, the timing of which corresponds to East African
rifting events. This has also been observed in other, albeit
terrestrial, taxa (e.g. chameleons, Matthee et al., 2004).
The phylogenetic hypothesis presented here also recovers
two main clades (A and B), and although the reality of
clade B is questionable, the divergence of these clades are
within a similar time frame: clade A 15.3 Ma (95% HPD:
12.5–18.7) and clade B 16.3 Ma (95% HPD: 13.5–19.7).
However, increased taxonomic sampling to previous
studies (Day & Wilkinson, 2006; Koblemüller et al.,
2006) highlights a complex biogeographic pattern of this
catfish clade, with no geographic region strictly monophyletic. African cichlid fishes also show a complicated
biogeographic history (Genner et al., 2007).
Our data reveal that although clade A contains a
greater proportion of East African taxa, it is by no means
exclusively so, containing representatives from West, and
central, and southern river systems (Fig. 3). With the
exception of the ‘southern African’ flock and the East
African S. afrofischeri, clade B is composed of West and
central African taxa. Notably divergence estimates for
these taxa are relatively young, suggesting that colonization into different geographic regions ⁄ river systems has
occurred relatively recently. Thus, although rifting
events may have been responsible for the initial divergence within Synodontis, dispersal has been dominant in
their subsequent evolutionary history.
Our phylogenetic hypothesis reveals that Synodontis
have colonized southern Africa from two different
lineages and that judging from the chronogram (Fig. 3)
this has occurred more recently in their history. Divergence of the ‘southern African’ flock from its most recent
common ancestor (MRCA) occurred 7.7 Ma (95% HPD:
5.8–10.3), whereas S. nigromaculata and S. zambezensis
diverged from their MRCA 6.5 Ma (95% HPD: 4.7–8.5).
The timings of these two invasions, particularly taking
into account 95% confidence intervals, lend support that
colonization occurred at a similar time. The MRCA of the
former clade are Congolese taxa, and it is known that
sections of the river system south of the Congo basin (e.g.
Zambezi and Okavango networks) have belonged to the
palaeo-congo network (Stankiewicz & de Wit, 2006).
Colonization from East to southern Africa is more
complicated, although the occurrence of the S. nigromaculata species complex in southern Africa as well as LT
drainage, suggests fish-accessible waterways throughout
this region (Koblemüller et al., 2006). Clearly, denser
sampling of Synodontis along with quantitative biogeo-
813
graphic analyses will shed more light upon their phylogeographic history.
Acknowledgments
JJD is supported by a Dorothy Hodgkin Royal Society
Fellowship and this study was financed by NERC grant
NE ⁄ F000782 ⁄ 1. We thank C. Cox (NHM) for help and
implementation of P4 software. JJD thanks the Fisheries
Resources Research Institute (FIRI), Jinja, Uganda, in
particular J. Balirwa and G. Namulemo and M. Wilkinson (NHM) for field assistance. I. Payne and R. Wakeford
(MRAG, Ltd) are thanked for tissue samples.
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Appendix 1 Provenance, voucher and GenBank accession data for samples (59 taxa) used in phylogenetic analyses.
Accession numbers
GenBank
Species
First described
Country
Locality
Water body
Vouchers
Cyt b
rpS7
Microsynodontis sp.
Chiloglanis
asymetricaudalis
Synodontis
East Africa
S. afrofischeri
S. afrofischeri
S. af. afrofischeri
S. af. ilebrevis
S. irsacae
S. frontosa1
S. frontosa2
S. frontosa3
S. frontosa4
S. frontosa5
S. frontosa6
S. grandiops
Boulenger 1903
De Vos 1993
C
TZ
Cuvette-Ouest
Kigoma
Lékénie river
Mukuti Bridge
CU 89213
CU 90429
DQ886604
FM878873
–
–
U
U
TZ
TZ
ZM
U
U
U
U
U
U
TZ
Lake Victoria
Lake Albert
Malagrasi river
Lake Tanganyika
Lake Tanganyika
Lake Albert
Lake Albert
Lake Albert
Lake Albert
Lake Albert
Lake Albert
Lake Tanganyika
BMNH 2006.3.6.34* (5550)
BMNH 2007.8.29.31 (5547)
CU 90419
BMNH 2006.3.6.25 (5153)
BMNH 2006.3.6.20 (5053)
BMNH 2007.8.29.19 (5540)
BMNH 2007.8.29.20 (5541)
BMNH 2007.8.29.21 (5542)
BMNH 2007.8.29.22 (5543)
BMNH 2007.8.29.23 (5544)
Tissue only
CU 91902
DQ886618
FM878842
DQ886616
DQ886644
DQ886653
FM878851
FM878850
FM878852
FM878853
FM878854
FM878876
FM878846
FM878890
FM878917
FM878889
FM878902
FM878900
FM878913
FM878912
FM878914
FM878915
–
–
FM878897
TZ
TZ
ZM
MW
U
Jinja
Wanseko
Kigoma
Sibwesa
Mpulungu
Wanseko
Wanseko
Wanseko
Wanseko
Wanseko
Wanseko
Jakobsen’s
Beach
Ikola
Kigoma
Mpulungu
Nkhata Bay
Wanseko
Lake
Lake
Lake
Lake
Lake
UF 160945
BMNH 2006.3.6.15 (5126)
BMNH 2006.3.6.9 (5143)
BMNH 2006.3.6.1 (4766)
BMNH 2007.8.29.24 (5546)
DQ886651
DQ886631
DQ886625
DQ886620
FM878855
FM878898
FM878903
FM878896
FM878907
FM878880
Borodin 1936
Boulenger 1906
ZM
ZM
TZ?
U
U
MZ
TZ
U
Mpulungu
Mpulungu
n.a.
Lake Albert
Wanseko
Niassa Area
Kigoma
Jinja
Lake Tanganyika
Lake Tanganyika
n.a.
Lake Albert
Lake Albert
Lugenda river
Lake Tanganyika
Lake Victoria
BMNH 2006.3.6.29 (5145)
BMNH 2006.3.6.21 (5100)
BMNH 2007.8.29.25 (5537) (Tr)
BMNH 2007.8.29.26 (5545)
Tissue only
SAIAB 73898
CU88758
BMNH 2006.3.6.14 (5518)
DQ886638
DQ886645
FM878847
FM878849
FM878848
FM878859
DQ886658
DQ886657
FM878901
FM878899
FM878909
FM878911
FM878910
FM878906
FM878904
FM878908
Schilthuis 1891
Poll 1959
C
C
n.a.
n.a.
n.a.
n.a.
BMNH 2006.3.6.35 (Tr)
BMNH 2006.3.6.36 (Tr)
DQ886605
DQ886606
FM878882
FM878883
S.
S.
S.
S.
S.
granulosa
lucipinnis
multipunctata
njassae
nigrita
S. petricola
S. polli
S. af. punctulata
S. serrata1
S. serrata2
S. sp. nov
S. af. tanganaicae
S. victoriae
Central Africa
S. angelica
S. brichardi
Cuvier 1817
Hilgendorf 1888
Wright & Page 2006
Wright & Page 2006
Vaillant 1895
Wright & Page 2006
Boulenger 1900
Matthes 1959
Boulenger 1898
Keilhack 1908
Cuvier & Valenciennes
1840
Wright & Page 2006
Matthes 1959
Günther 1889
Rüppell 1829
Tanganyika
Tanganyika
Tanganyika
Malawi
Albert
ª 2009 THE AUTHORS. J. EVOL. BIOL. 22 (2009) 805–817
JOURNAL COMPILATION ª 2009 EUROPEAN SOCIETY FOR EVOLUTIONARY BIOLOGY
816
J. J. DAY ET AL.
Appendix 1 (Continued)
Accession numbers
GenBank
Vouchers
Cyt b
rpS7
n.a.
Mambili river
Lékénie river
Lékoli river
Congo river
Luapula river
Chambeshi river
Cuvette-Ouest Lékoli river
Cuvette-Ouest Mambili river
Sud
Lobé river
Cuvette-Ouest Congo river
Luapula
Lake Mwueru
CU 91408
CU 88252
CU 87469
CU 88152
AMNH 235728
CU 91002
CU 91003
CU 87539
CU 87571
CU 89984
AMNH 235730
CU 91011
FM878875
DQ886607
DQ886608
DQ886609
DQ886610
FM878856
FM878857
DQ886611
DQ886612
DQ886613
DQ886614
FM878874
FM878925
FM878885
FM878881
FM878884
FM878894
–
–
FM878887
FM878886
FM878877
FM878888
FM878891
BW
BW
MZ
MZ
Boulenger 1905
BW
ZM
ZM
ZM
BW
Skeleton & White 1990 BW
BW
Boulenger 1911
BW
Peters 1852
MZ
Okavango
Okavango
Manica Area
Manica Area
Okavango
Luapula
Luapula
SAIAB 68779
SAIAB 68679
SAIAB 67669
SAIAB 67674
SAIAB 52275
CU 91094
CU 91092
CU 91099
SAIAB 52277
SAIAB 68674
SAIAB 68675
SAIAB 68721
SAIAB 64838
FM878860
FM878867
FM878862
FM878863
DQ886615
FM878845
FM878843
FM878844
FM878861
FM878865
FM878864
FM878866
FM878858
FM878918
FM878923
–
FM878920
FM878895
Okavango
Okavango
Okavango
Okavango
Maputo area
Thoage river
Okavango river, Maunachira
Buzi river
Buzi river
Thoage river
Lake Bangwuelu
Luapula river
Chambeshi river
Thoage river
Okavango river, Boro
Okavango river, Boro
Maunachira river
Maputo river
Günther 1864
Poll 1971
Magburaka
Magburaka
Magburaka
Bumbuna
Bumbuna
Rokel
Rokel
Rokel
Rokel
Rokel
Tissue only (5765)
FM878868
Tissue only (5530)
FM878872
Tissue only (5531)
FM878871
BMNH 2007.8.29.6 (5535) FM878869
BMNH 2007.8.29.7 (5536) FM878870
Species
First described
Country Locality
S. clarias
S. congica
S. contracta
S. decora
S. greshoffi
S. katangae
S. katangae
S. nigriventris
S. pleurops
S. rebeli
S. soloni
S. unicolor
Southern Africa
S. leopardina
S. macrostiga
S. nebulosa
S. nebulosa
S. nigromaculata1
S. nigromaculata2
S. nigromaculata3
S. nigromaculata4
S. af. thamalakalensis
S. vanderwaali
S. vanderwaali
S. woosnami
S. zambezensis
West Africa
S. gambiensis
S. thysi
S. thysi
S. waterloti1
S. waterloti2
Linné 1758
Boulenger 1901
Vinciguerra 1928
Boulenger 1899
Schilthuis 1891
Boulenger 1901
CAR
C
C
C
C
ZM
ZM
C
C
CR
C
ZM
David 1936
Boulenger 1897
Holly 1926
Boulenger 1899
Boulenger 1915
Pellegrin 1914
Boulenger 1911
Peters 1852
Daget 1962
SL
SL
SL
SL
SL
Water body
Nana-Grébiz
Cuvette-Ouest
Cuvette-Ouest
Cuvette-Ouest
Cuvette-Ouest
Luapula
river
river
river
river
river
FM878892
FM878893
FM878919
–
FM878921
FM878922
FM878905
FM878924
FM878916
FM878878
FM878879
Superscript numbers denote individuals of the same species.
Locality codes. B, Botswana; CAR, Central African Republic; CR, Cameroon; C, Congo; MW, Malawi; MZ, Mozambique; SL, Sierra Leone;
TZ, Tanzania; U, Uganda; ZM, Zambia; n.a., not available.
Repository codes. AMNH, American Museum of Natural History; BMNH, The Natural History Museum, London; CU, Cornell University Museum
of Vertebrates; SAIAB, South African Institute for Aquatic Biodiversity; UF, Florida Museum. Numbers in parenthesis = JJD field tags. Tr = fish
acquired through aquarium trade.
Note on taxonomy. Following Wright & Page (2006), the ‘dwarf form’ of S. petricola (Day & Wilkinson, 2006) is now referred to as
S. lucipinnis, whereas S. af. petricola is referred to here as S. petricola. Specimens described as S. dhonti in previous studies are now referred
to as S. irsacae, as S. dhonti is only known from a single specimen. It should also be noted that we follow the taxonomic names outlined
in Ferraris (2007), in which species names are now feminine.
ª 2009 THE AUTHORS. J. EVOL. BIOL. 22 (2009) 805–817
JOURNAL COMPILATION ª 2009 EUROPEAN SOCIETY FOR EVOLUTIONARY BIOLOGY
Lacustrine radiations in African Synodontis catfish
817
Appendix 2 Locality and GenBank accession data for samples common to the data sets of *Day & Wilkinson (2006), Koblemüller et al. (2006)
and this study.
GenBank accession numbers
Taxon
Locality
Cytochrome b
Control region
ND6
S7 intron 1
S.
S.
S.
S.
S.
S.
S.
S.
S.
S.
S.
S.
Congo river, n.a.*; CAR
Congo river, n.a.*; CAR
Congo river, C*; CAR
Thorage river, BW*; Lake Mweru, ZM
LM
LV
LT
LT
LT
LT
LT
LT
DQ886605
DQ886606
DQ886611
DQ886615
DQ886620
DQ886657
DQ886651
DQ886653
DQ886631
DQ886625
DQ886638
DQ886645
DQ662944
DQ662943
DQ662941
DQ662954
DQ663012
DQ663013
DQ662962
DQ662997
DQ662989
DQ662963
DQ662977
DQ662987
DQ663033
DQ663035
DQ663030
DQ663043
DQ663077
DQ663059
DQ663053
DQ663056
DQ663051
DQ663046
DQ663050
DQ663052
FM878882
FM878883
FM878887
FM878895
FM878907
FM878908
FM878898
FM878900
FM878903
FM878896
FM878901
FM878899
angelica
brichardi
nigriventris
nigromaculata
njassae
victoriae
granulosa
irsacaeà
lucipinnis§
multipunctata
petricola
polli
Note that voucher specimens from independent author studies are not the same. With the exception of S. nigromaculata, specimens are from
similar localities. àS. dhonti in previous studies, §S. petricola (Day & Wilkinson, 2006); S. sp. nov. (Koblemüller et al., 2006).
Received 4 September 2008; revised 8 December 2008; accepted 18 December 2008
ª 2009 THE AUTHORS. J. EVOL. BIOL. 22 (2009) 805–817
JOURNAL COMPILATION ª 2009 EUROPEAN SOCIETY FOR EVOLUTIONARY BIOLOGY