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ISSN 0016-6707, Volume 138, Number 6
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Pre-zygotic factors best explain reproductive isolation betweenthe hybridizing species of brittle-stars Acrocnida brachiataand A. spatulispina (Echinodermata: Ophiuroidea)
D. Muths • D. Davoult • M. T. Jolly •
F. Gentil • D. Jollivet
Received: 23 April 2009 / Accepted: 8 February 2010 / Published online: 7 March 2010
� Springer Science+Business Media B.V. 2010
Abstract The two brittle-stars Acrocnida brachiata
(Montagu 1804) and A. spatulispina (Stohr and Muths in J
Mar Biol Assoc, 2009) exhibit strong spatial segregation
along the coast of Brittany (France), the first being subti-
dally distributed relative to the other intertidal species.
Despite a very high degree of mitochondrial DNA diver-
gence, previous preliminary results hinted at the potential
for hybridization to occur. Therefore, we specifically aim
to determine local levels of hybridization between these
two species and to investigate the relative roles of pre- and
post- zygotic isolation processes acting to decrease local
hybridization patterns. Mitochondrial DNA, allozymes and
the Internal Transcribed Spacer 2 region of the ribosomal
DNA were all used on 529 brittle-stars sampled locally in
June and September 2005, among six stations in Dou-
arnenez Bay, a site situated at the tip of Brittany. Only
2.6% of all samples analyzed were identified as potential
hybrids. However, these were twice more frequent in June,
just after the reproductive period, than in September after
selective mortality acted to reduce the proportions of
hybrids. In addition to the abrupt bathymetric segregation
between the two species, spawning asynchrony also clearly
restricts hybridization to low levels, which shows the
importance of pre-zygotic mechanisms in maintaining
reproductive isolation. Moreover, both limited hybridiza-
tion events and adult mortalities following reproduction
tend to generate local genetic differentiation at the intra-
species level. On the contrary, the genetic structure is
homogenized by migration of juveniles or adults and
hybrids mortalities over the summer period.
Keywords Hybridization � Migration � Mortality �Spatio-temporal isolation
Introduction
Genetic studies using echinoderms have highlighted the
influence of larval dispersal on patterns of population
structure in the marine environment (e.g. Palumbi et al.
1997; Arndt and Smith 1998), led to calibrate gene-specific
rates of molecular evolution (Bermingham and Lessios
1993) and to delineate species boundaries (Knowlton
1993). In the latter case, such studies have either enabled
the recognition of synonymous taxa (the sea cucumber
Cucumaria sp. Arndt et al. 1996 and the sea star Patiriella
sp. O’Loughlin et al. 2002) or the identification of species
complexes within otherwise morphologically described
species (the sea star Parvulastra exigua Hart et al. 2006,
the sea urchin Echinocardium cordatum, Chenuil and Feral
2003 and the brittle-star Amphipholis squamata, Boissin
et al. 2008). Similarly, a phylogeographic study of the
brittle-star Acrocnida brachiata (Muths et al. 2006) pre-
sented evidence for the existence of two potentially cryptic
D. Muths � D. Davoult � F. Gentil � D. Jollivet
UPMC Univ Paris 6, UMR 7144, BP 74, 29680 Roscoff cedex,
France
D. Muths � D. Davoult � F. Gentil � D. Jollivet
CNRS UMR 7144, Station Biologique de Roscoff, BP 74, Place
Georges Teissier, 29682 Roscoff cedex, France
M. T. Jolly
The Marine Biological Association of the United Kingdom,
The Laboratory, Citadel Hill, Plymouth, Devon PL1 2PB, UK
Present Address:D. Muths (&)
IFREMER Delegation Reunion, Rue Jean Bertho,
97822 Le Port cedex, France
e-mail: [email protected]
123
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DOI 10.1007/s10709-010-9441-4 Author's personal copy
Page 3
species with a clear bathymetric ‘‘intertidal versus subtid-
al’’ segregation at sympatric locations along the western
entrance of the English Channel. A morphological inves-
tigation (Stohr and Muths 2009) recently assessed the
status of A. brachiata as previously described by Montagu
(1804) and actually diagnosed the original type as the
subtidal species. The intertidal lineage was characterized as
a new species named Acrocnida spatulispina in reference
to its spatula-shaped arm spines which is one of the iden-
tification criteria.
Both Acrocnida species are common dwellers of soft
sediments habitats along the North Western European
coastlines. A. brachiata is widely distributed in the
Northeast Atlantic, from the Mediterranean to the shelf
seas around the British Isles, but is never encountered
above 56�N (Koehler 1921). It is often observed as
densely populated aggregates among subtidal habitats
(1,000 ind.m-2 in Ireland, Keegan and Mercer 1986,
900 ind.m-2 along the coast of Normandy, Gentil and
Zakardjian 1989). On the contrary, the presence of
A. spatulispina is seemingly restricted to the intertidal zone
of the Irish sea and the Brittany coastline, where popula-
tions are more sparsely distributed (fewer than
100 ind.m-2 in Brittany, Bourgoin 1987; D. Muths, per-
sonal observation). Despite strong differences in habitat
preferences, it is unlikely that diversifying selective pro-
cesses were directly implicated in the initial separation of
the two lineages. Their emergence is reportedly linked to
large scale vicariance that affected cladogenetic events
similarly among a variety of boreal species belonging to
muddy-fine sediment communities (Jolly et al. 2006;
Muths et al. 2006). This vicariance hypothesis as opposed
to ecotypic speciation is supported by two observations
favouring the secondary contact hypothesis. Firstly,
bathymetric segregation of the two species may be differ-
ent since sampling undertaken in the intertidal zone in
south Brittany (Forest Bay) clearly identified the species
occurring subtidally at the western entrance of the English
Channel (i.e. Acrocnida brachiata). Secondly, neither
species exhibit total reproductive isolation as few individ-
uals displayed a mitochondrial haplotype of one species
and the nuclear background of the other.
How and in which frequency such evolutionary lineages
are able to hybridize despite deep mitochondrial diver-
gence (19.6% based on the COI gene, Muths et al. 2006)
have yet to be determined. In this context, it is important to
note that both temporal and spatial differences in spawning
patterns are often cited as one of the primary mechanisms
contributing to pre-zygotic isolation between closely-
related, broadcast-spawning marine species (e.g. Palumbi
1994). This therefore makes it essential to understand the
extent to which spatial restriction of Acrocnida sp. adults
and temporal isolation may act to limit cross-mating but
still maintain incomplete reproductive isolation between
the two species. Generally speaking, recruitment processes
among Acrocnida sp. populations near the western entrance
of the English Channel (Douarnenez Bay, see Fig. 1) have
been relatively well-studied mainly because of their geo-
graphic location and high densities (Bourgoin et al. 1991).
Moreover, the western entrance of the English Channel
might represent a tension zone between the two cryptic
species, with the potential for localised hybridization
(Muths et al. 2006). In fact, not only does the Brittany
coastline lie within a transition zone between boreal
Fig. 1 Geographic distribution
of the two species along
European coasts (according to
Muths et al. 2006 and Stohr and
Muths 2009). Acrocnidaspatulispina and A. brachiataare respectively represented by
black and white items. Squaresand circles represent
respectively intertidal and
subtidal sampling sites. Rightmap: the location of the six
sampling stations in
Douarnenez Bay, along two
transects A and B. Each transect
included one station in the
intertidal zone (zero meter
depth: 0A and 0B) and two in
the subtidal zone, at ten and
thirty meters depth (10A, 10B,
30A, 30B)
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(cold-temperate) and lusitanian (warm-temperate) assem-
blages (Cabioch 1968) but the occurrence of tension zones
with mosaically distributed hybrid zones (Mytilus sp.:
Bierne et al. 2003) sharp genetic breaks associated with
contemporary hydrodynamic features (Pectinaria koreni:
Jolly et al. 2005) and habitat suitability (Hydrobia sp.:
Wilke and Pfenninger 2002) have also all been documented.
In addition to the evidence of highly divergent lineages,
Muths et al. (2006) demonstrated that the very short larval
phase (no more than 4 days) largely restricted gene flow
within each species, even between neighbouring popula-
tions. No clear pattern of isolation-by-distance was detec-
ted at macro-geographic scales, which may be an
indication of the predominant role of local scale processes
in masking larger scale genetic patterns (Hellberg et al.
2002). As such, this study also aimed to identify different
migration scenarios.
We employed a targeted approach based on large sample
sizes for well-defined spatial units of Acrocnida sp. col-
lected along a locally restricted bathymetric gradient (less
than 20 km) in Douarnenez Bay. Using transects, genetic
variation was assessed to determine the extent of hybrid-
ization between the two species and to identify potential
patterns of segregation in the spatio-temporal distribution
of parental and hybrid adults. Hybrid diagnosis involved
using the Internal Transcribed Spacer 2 region of the
ribosomal DNA (ITS2) restriction profiles together with
analysis of nucleo-cytoplasmic disequilibrium. The role of
spatial distribution and spawning asynchrony as pre-
zygotic barriers to cross-breeding were also tested. More-
over, using temporal samples collected throughout the
reproductive period should facilitate the detection of
potential counter-selection of hybrids during the course of
the summer period and its influence as a further post-
zygotic barrier preventing genotypes from becoming fixed
in the local population. Finally, this micro-spatial sampling
also served to better determine the mechanisms that influ-
ence the genetic structure within each species.
Materials and methods
Sampling
Samples were collected in 2005 and 2006 along two
transects (Fig. 1) spanning a bathymetric gradient of
30 meters. Each included three stations: one situated in the
intertidal at the lowest tidal limit on the shore (zero meter
depth) and two in subtidal areas at depths of 10 and 30 m,
respectively. Subtidal samples were obtained by sampling
the top 10 cm of sediment with a 0.25 m2 Hamon grab
(‘‘Ophirois’’ cruise) while intertidal samples were collected
by digging at low tide. Despite using a 2 mm-mesh sieve,
all individuals sampled had a disc diameter greater than
7 mm (measured using a binocular and a micrometer).
According to Bourgoin et al. (1991), such individuals
cannot be categorised as newly recruited individuals but as
two-years old adults.
To allow comparative genetic analyses, samples were
collected twice in both habitats, at similar dates in 2005, in
June (during or just after reproduction) and September
(well after reproduction). These dates were found appro-
priate as most of the recruitment process in Douarnenez
Bay occurs in late spring (Bourgoin et al. 1991; present
data). A time series of samples were collected in spring
2006, at one intertidal and one subtidal locality for com-
parison of gonadic development between the two species.
While all specimens from 2005 were whole frozen in
liquid nitrogen for genetic analysis, those collected in 2006
were dissected to quantify the extent of gonad maturity.
Genetic data acquisition
A total of 529 individuals from the two species of
Acrocnida sp. were fingerprinted using sequences of the
mitochondrial Cytochrome Oxidase I gene (COI), restric-
tion profiles of the ribosomal ITS2 internal spacer and
genotypes of five enzyme systems. For each individual, the
disc-shaped body was used for enzymatic starch gel elec-
trophoresis, and the arms for DNA extraction and
sequencing.
Mitochondrial COI sequencing
Specific primers Ab-COIf and Ab-COIr (Muths et al. 2006)
were used to amplify a 598-bp fragment of the COI gene.
Details of the COI amplification and sequencing proce-
dures are described in Muths et al. (2006). Sequences were
run along both directions, then edited using Chromas ver-
sion 1.6 (McCarthy 1997) and aligned using ClustalW
(Thompson et al. 1994) implemented in BioEdit Sequence
Alignment Editor (Hall 1999).
Amplification of the internal transcribed spacer 2 (ITS2)
and restriction fragment length polymorphisms (RFLPs)
Amplification of ITS2 was performed using primers
developed by P.W. H. Holland and collaborators (see
Jollivet et al. 1998). Reactions were performed in 27 ll
containing PCR buffer (19), 1 mM MgCl2, 12.5 lM of
each dNTP, 0.3 lM of each primer, 0.5 U of Thermoprime
Plus Taq polymerase (Abgene), 25 ng CTAB-extracted
genomic DNA. Cycling parameters were 94�C for 5 min,
followed by 40 cycles of 94�C for 45 s, 50�C for 60 s, and
72�C for 60 s and a final elongation at 72�C for 7 min.
PCR products of ten individuals of each lineage were
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cloned into a pGEM-T vector, using a Promega pGEM161
T cloning kit (Promega, Madison, WI, USA). Sequencing
of plasmid inserts was performed using universal M13
primers flanking the inserted fragment, and sequences were
submitted to GenBank (Accession nos EU431193–
EU431216). The amplified 535-bp sequences of the ITS2
rDNA displayed seven fixed mutations between Acrocnida
spatulispina and A. brachiata. To discriminate individuals
of each lineage and their potential hybrids, restriction
profiles were identified using a set of three restriction
enzymes (SmlI, Eco88 and XhoI). Enzyme digestions were
carried out according to the manufacturer’s instructions
(Biolabs), using 5 ll of amplified template from each of
the 529 individuals collected. RFLP profiles were then
visualised on a 4% agarose gel made up of TBE (19).
Starch gel electrophoresis
Electrophoretic procedures were performed according to
Pasteur et al. (1987), and the following five enzymatic
systems were used: Glucose Phosphate Isomerase (PGI,
E.C. 5.3.1.9), Mannose Phosphate Isomerase (MPI, E.C.
5.3.1.8), Malic Enzyme (ME, E.C. 1.1.1.40), Phosphoglu-
comutase (PGM, E.C. 5.4.2.2) and Hexokinase (HK, E.C.
2.7.1.1). Frozen samples of the body were homogenized in
250 ll grinding buffer (10 mM Tris–HCl, 2 mM EDTA,
0.05% b-mercaptoethanol, 0.1 mM PMSF, 0.25 mM
sucrose; pH 6.8), centrifuged at 6,500g for 12 min, and the
supernatant stored at -80�C until electrophoresis. Hori-
zontal enzyme electrophoresis was conducted on 12%
starch gels using the following buffers: (1) Tris–Borate-
EDTA (pH 8.6) for PGI, MPI and ME and (2) Tris–HCl
(pH 8.5) for the PGM and HK. Buffer systems were run at
constant amperage, during 5 h (160 V, 35 mA for system
(1) and 150 V, 40 mA, for system (2)). The most frequent
allele was labelled ‘100’ and all others were labelled
according to their relative mobility from allele 100.
Population genetic analyses
All analyses were made in parallel for the two species. For
each station, haplotype (HD) and nucleotide (p) diversities
were estimated with DNAsp 4.0 (Rozas et al. 2003).
Pairwise values of haplotypic frequency-based differenti-
ation (FST) were calculated using ARLEQUIN 2.0
(Schneider et al. 2001).
For the allozyme dataset, the allele frequencies per
population, together with the observed (HO) and expected
(HNB) heterozygosities were all estimated using GENEPOP
3.4 software (Raymond and Rousset 1995). Allelic richness
(RS) was further estimated using FSTAT 2.9.3.2 (Goudet
1995) based on a diploid number of 22 individuals.
Deviations from Hardy–Weinberg equilibrium expecta-
tions were tested for each population at each locus. This
was achieved by calculating Wright’s fixation index FIS as
estimated by Weir and Cockerham (1984) and departures
from Hardy–Weinberg equilibrium tested using Fisher’s
exact tests implemented in GENEPOP 3.4. The null
hypothesis of independence between loci was tested from
genotypic disequilibrium analyses using the same software.
Genetic differentiation between pairwise combinations of
samples from each station and from each sampling date
was estimated by calculating Weir and Cockerham’s
(1984) h for each locus and between stations and sampling
dates. The Waples’ (1989) test was also used to estimate
the effect of drift on temporal changes in allele frequencies.
As sampling was undertaken after reproduction, analyses
were conducted according to sampling plan I (individuals
taken after reproduction; see Waples 1989). Using
TEMPTEST 2.2 (Waples 1989), calculations were made
locus by locus, using frequencies of the two most common
alleles. A third ‘‘combined’’ category included all other less
frequent alleles. As the effective population size (Ne) was
unknown, each test was performed using five Ne values
ranging from 50 to 1,000, which seems a reasonable range
given published census data. The null hypothesis of no
change was rejected if changes in allele frequencies
between sampling dates were significantly greater than
expected under conditions of random genetic drift alone.
To estimate the robustness of allozyme divergence
between mitochondrial lineages, exact tests of cytonuclear
disequilibrium were conducted using the CNDM program
(Asmussen and Basten 1994; Basten and Asmussen 1997).
Allozymes significantly correlated to each species were
then used to reconstruct a hybrid index (HdI) in order to
detect putative hybrids in the collected sample. For each
diagnostic allele identified with CNDM, a score of -1 or
?1 was respectively assigned to the characteristic forms of
A. spatulispina and A. brachiata, respectively. With only
three diagnostic loci per species, cumulative HdI values
ranged from -5 to ?6. With nine diagnostic loci for A.
brachiata versus five for A. spatulispina, the central value
was not 0 but closer to 2. Thus, individuals of A. spatu-
lispina displaying an HdI greater or equal to 2 can be
considered as potential hybrids. Conversely, the same
possibility may be expected for individuals of A. brachiata
yielding a HdI strictly lower than 2. The software
STRUCTURE 2.2 (Pritchard et al. 2000) was also used to
test the robustness of genetic isolation between Acrocnida
species and identify putative hybrids. The number of
populations was set from K = 2 to 6 (for the two species to
the 6 sampling sites). The optimal value of K was selected
based on Evanno et al. (2005). Simulations involved
100,000 Markov Chain Monte Carlo (MCMC) iterations
followed by a burn-in period of 100,000.
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Spatio-temporal survey of gonad maturity
Sexual maturity was determined for each species based on
the Gonadic Index (GI). The survey was undertaken for A.
spatulispina at station 0A and for A. brachiata at station
10A during the reproductive season, with samples collected
every 15 days, from mid-March 2006 to mid-July 2006.
For each sampling date and each species, ten males and ten
females were fixed in a ‘‘Bouin’’ solution (75% picric acid,
20% formaldehyde, 5% acetic acid; Bourgoin 1987). A
total of 270 individuals were dissected under a binocular
microscope. Gonads were separated from somatic tissue
and both were dried at 60�C for 24 h before being weighed
as dry weight (DW). GI was then estimated as the ratio of
DW of gonads to DW of whole body, and times 100 to give
percentage. Significant differences between sampling dates
were then tested using a Mann & Whitney U-test.
Results
As in Muths et al. (2006), a deep level of mitochondrial
COI divergence (19.6% according to K2-P distance;
Kimura 1980) was revealed between subtidal and intertidal
areas which correspond respectively to A. brachiata and
A. spatulispina. The analysis made with STRUCTURE
strongly suggested that the highest likelihood of obtaining
such data was to consider that two strongly separated
genetic entities existed (K = 2). Moreover, highly signifi-
cant cytonuclear disequilibria (P \ 0.001) were found
from four of the five allozyme loci, all except for the Me
locus (Table 1). However, 2.6% of all individuals analyzed
had a mitochondrial and nuclear genetic signature respec-
tively typical from opposite species. These elements con-
firmed that reproductive isolation is incomplete among
those evolutionary and morphologically divergent species,
at least in Douarnenez Bay. We therefore first searched
among the possible evolutionary mechanisms responsible
for maintaining low levels of hybridisation in the face of
strong spatial segregation, and vice versa. We then ana-
lyzed the genetic structure within each species.
Segregation between species
Bathymetric separation
The bathymetric segregation between the two species is
clear and abrupt, with intertidal or subtidal individuals
displaying completely different sets of haplotypes. In
addition, allozymes also exhibited strong differences
between species. The intertidal A. spatulispina samples had
two diagnostic alleles at the Hk locus: Hk-90 (only found
in A. spatulispina) and Hk-95 (present in only four
A. brachiata samples) (see Fig. 2a). Such exclusive alleles
were however not found to be significantly associated with
the intertidal lineage in the cytonuclear disequilibria
(Table 1). Likewise, in A. brachiata, despite one exception,
all the individuals sampled from subtidal areas (10 and
30 m depths) displayed either allele Hk-100 or Hk-105
(Fig. 2b). This spatial segregation was observed both in
June, just after reproduction, and in September, well after
the reproductive period. This emphasises the strong rela-
tionship between bathymetry and species distribution.
Spawning asynchrony
For all species and sampling dates, the Gonadic Index (GI)
was globally higher for males than for females, but dif-
ferences were never significant (Mann & Whitney U test,
P [ 0.05). Gonad maturation data were therefore pooled
within each site to perform comparisons between species at
each sampling date (Fig. 3). Over the 2006 summer period,
for Acrocnida brachiata, GI increased significantly in April
whereas for A. spatulispina, this increase began in early
May (Mann & Whitney test, U = 2.72 and 3.75, respec-
tively, with P \ 0.001). This increase in gonad maturation
was followed 1 month later, for both species, by an abrupt
drop associated with the release of gametes in the water
column. This induced significant differences in GI between
species during the following months (P \ 0.001). Gamete
release was detected in May for A. brachiata (U = 4.63;
P \ 0.001) and in early June for A. spatulispina
(U = 3.26; P \ 0.001). Overall, the time series of both
species show a clear spawning asynchrony of about
15 days between both species.
Hybridization between species and distribution of hybrids
Out of a total of 529 individuals, the proportion of hybrids
detected using ITS2 restriction profiles was only 0.95%, i.e.
five individuals (results summarized in Table 2). This excess
Table 1 Cytonuclear linkage disequilibrium for the two Acrocnidaspecies: between mitochondrial sequences and enzyme alleles, esti-
mated using CNDM software (Asmussen and Basten 1994; Basten
and Asmussen 1997)
Associated alleles mtDNA Type P
A. spatulispina A. brachiata
HK 80 100/105/110 < 0.001
PGM 90 104/110/116 < 0.001
PGI – 90/104/108 < 0.001
ME – – 0.93
MPI 70 – < 0.001
Values in bold show which alleles of each locus is significantly
associated with each species
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of parental types and deficiency of recombinants is illus-
trated by significant cytonuclear disequilibrium (Table 1).
The five ITS2 profiles that were identified as potential
hybrids all displayed an A. spatulispina mitochondrial
haplotype but, based on the hybrid index, only four indi-
viduals displayed an A. brachiata nuclear background. All
four were sampled in the intertidal habitat (station 0A) in
June. On the contrary, the remaining hybrid detected with
ITS2 showed a clear mitochondrial and nuclear genetic
signature of A. spatulispina and was sampled in the subtidal
station (station 10B) in September. This shows that a strong
spatial segregation between hybrid types might also occur, at
least just after reproduction in June.
Strictly based on the hybrid index (see Fig. 4 and details in
Table 2), nine additional individuals could also represent
introgressed individuals. When the search for putative hybrids
was performed with STRUCTURE (Pritchard et al. 2000)
using five allozyme loci together with the ITS2 data, the same
nine individuals were identified as intermediate types.
On these 14 putative hybrids (2.6% of all individuals
analyzed), most were sampled in June from only two sta-
tions: one intertidal (0A, n = 4) and one subtidal (30B,
n = 5). The geographical distribution of hybrids was less
homogeneous in September, with five putative hybrids
found from four different stations (0A, 10A, 10B and 30B).
Temporal changes in the localisation of putative hybrids
could also be identified by looking at the temporal variation
Fig. 2 Haplotype and allozyme frequencies in A. spatulispina(Fig. 2a, n = 162) and A. brachiata (Fig. 2b, n = 367) Symbols ontop of histograms indicate when samples differ significantly between
June and September on the basis of a permutation test on the estimator
h of Weir and Cockerham (1984) (* P \ 0.05 and *** P \ 0.001) and
whether these differences are explained by drift alone on the basis of
the Waples’ (1989) test with ¤ (¤ \ 0.05 and ¤¤¤ \ 0.001).
Concerning haplotype frequencies (in top left corner), HIi and HSi
are the more frequently found haplotypes in A. spatulispina and
A. brachiata respectively. Sh. corresponds to shared haplotypes
(found in more than one population of a given species but at low
frequency). Priv. corresponds to private haplotypes (found in only one
population). Concerning allozyme frequencies, the allele labeled 100
refers to the most frequent one
0
20
40
60
03/17
/06
04/13
/06
04/26
/06
05/15
/06
05/29
/06
06/16
/06
07/13
/06
Gon
daic
inde
x (G
I, %
)
* **
*
Fig. 3 Time series showing the evolution of the Gonadic Index (GI)
in the two Acrocnida species sampled in Douarnenez Bay (n = 270).
Bold and standard lines represent A. brachiata and A. spatulispina,
respectively. * indicates a significant difference in GI, at a given date
672 Genetica (2010) 138:667–679
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in the frequencies of ‘diagnostic’ alleles between sampling
dates (e.g. Hk-100 and Hk-105 in station 0A and Hk-95 in
station 30B; see Fig. 2).
Spatial and temporal genetic variation within Acrocnida
spatulispina
While mitochondrial sequences displayed high levels of
haplotype (HD) and nucleotide (p) diversities at both
intertidal stations surveyed (see values in Table 3), both
mean values were lower in June than in September. This
decrease was associated with the appearance of a new
haplotype (HI5) and an increase in the frequency of hap-
lotype HI4 at both intertidal stations in September
(Fig. 2a). Nevertheless, the proportion of shared and
‘‘private’’ haplotypes did not vary significantly between
sampling dates, resulting in non-significant temporal
genetic differences in pairwise FST estimates obtained from
mtCOI data (Table 4a).
The number of alleles at the five polymorphic enzyme loci
screened varied from 3 to 6, with an average of 4.8. Whereas
allelic richness (RS) was similar stations and sampling dates,
allelic frequencies (f, Fig. 2a) differed significantly between
stations and sampling dates. For example, at both intertidal
stations, the frequency of Pgi-104 increased significantly
from June to September, and inversely for Pgi-100. The
frequency of Me-100 at station 0B also increased signifi-
cantly from 50 to 84% between June and September, with a
concomitant decrease in Me-110. For the Me, frequencies
only remained constant at station 0A. Taken together, allele
frequencies between the two intertidal stations were far more
similar in September (h = 0.002, P [ 0.05, Table 4c) than
they were in June (h = 0.099, P \ 0.001, Table 4c), just
after reproduction. Values of temporal genetic differentia-
tion were also highly significant for both stations
(P \ 0.001) and were mostly associated with significant
monolocus P-values in the Waples’ test (1989; Fig. 2a). The
observed heterozygosity (HO) was higher than the expected
value (HNB) in September but not in June. Generally, there
were no significant deviations from Hardy–Weinberg equi-
librium expectations. Heterozygote deficiencies were only
observed in June for station 0B (Table 5).
Spatial and temporal genetic variation within Acrocnida
brachiata
Both haplotype (HD) and nucleotide (p) diversities were
higher in A. brachiata than in A. spatulispina (Table 3).
Pairwise FST estimates (Table 4b) indicated that most
values of genetic differentiation were low and non-signif-
icant for subtidal stations, except between stations 10B and
Table 2 Hybrid diagnosis
between Acrocnida species
The following details are given
for the 14 putative hybrids: the
sampling dates and stations; the
mtDNA signature (As for A.spatulispina, Ab for A.brachiata); the respective
genotypes at the 5 allozyme loci
and the corresponding
hybridization index (HdI: values
strictly lower than 2 or higher
than 2 respectively indicates A.brachiata or A. spatulispinanuclear background); the ITS2
restriction profiles (As for A.spatulispina, Ab for A.brachiata, H for Hybrid)
Month Station mtDNA HK PGM PGI ME MPI Hdl ITS2
0A As 090095 100104 100100 100110 090100 -1 H
June 0A As 100100 100100 100104 100100 090100 3 H
0A As 100100 100104 100104 100100 090100 4 H
0A As 100105 100104 100100 100100 090100 3 H
Sept. 0A As 090100 100104 100104 100110 090090 2 As
30B Ab 100105 100100 100100 100100 070100 1 Ab
30B Ab 100105 100100 100100 100110 070100 1 Ab
June 30B Ab 095105 096104 100100 110110 100100 1 Ab
30B Ab 095105 100100 100100 100100 100100 0 Ab
30B Ab 095105 100104 100100 100100 100100 1 Ab
10B Ab 100105 110110 100108 100100 090100 5 H
Sept. 10A Ab 100105 090100 100100 100100 100100 1 Ab
10B Ab 105105 100100 100100 110110 070090 1 Ab
30B Ab 100105 100104 100100 100100 070070 1 Ab
0
50
100
-6 -5 -4 -3 -2 -1 0 1 2 3 4 5 6
Hybrid index (HDi)
Nb
of
ind
ivid
ual
s
A.spatulispina
A. brachiata
Fig. 4 Frequency distribution of the hybridization index HdI in the
whole sampling period of 2005, based on the result of the CNDM
software (Asmussen and Basten 1994; Basten and Asmussen 1997).
Extreme negative scores correspond to a nuclear background of
‘pure’ A. spatulispina whereas extreme positive scores to ‘pure’
A. brachiata. The Y axis represents the number of individuals of each
species
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Table 4 Spatial and temporal genetic differentiation within each Acrocnida species
(4b) 10 A 10 B 30 A 30 B(4a) 0A 0B 10 A -0.005 0.001 0.001 -0.0050A 0.001 -0.034 10 B -0.003 0.006 0.023*** 0.0060B -0.019 -0.034 30 A -0.005 -0.003 -0.005 -0.002
30 B 0.005 -0.000 -0.005 -0.002
(4d)(4c) 0.023* 0.019* 0.032*** 0.0030A 0.060*** 0.002 0.035*** 0.027* 0.075*** 0.038***0B 0.099*** 0.051*** 0.033*** 0.052*** 0.010 0.014*
0.036* 0.018* 0.063*** 0.093***
A. spatulispina A. brachiata
0A 0B 10 A10 B30 A30 B
10 A 10 B 30 A 30 B
Allo
zym
esm
tDN
A
The two-first tables (Tables 4a, b) are based on mtDNA dataset (FST) and the two-second ones (Tables 4c, d) on allozymes (h) dataset. Tables 4a
and c are for A. spatulispina and Tables 4c and d for A. brachiata. White cells represent spatial estimates of differentiation obtained between
stations sampled in June 2005, and light grey cells represent estimates obtained in September 2005. Dark grey cells represent the temporal
genetic differentiation observed between June and September, for any given station. Tests of significance were performed for mtDNA data and
for allozymes with ARLEQUIN 2.0 (Schneider et al. 2001) and with GENEPOP 3.4 (Raymond and Rousset 1995) respectively: *P \ 0.05;
***P \ 0.001; after a Bonferroni correction, only values significant at P \ 0.001 remain significant
Table 3 Temporal variation in genetic diversity in Douarnenez bay, for both Acrocnida species, and for all sampling stations and dates (n is the
sample size)
Species Station June September
n HD P RS HNB HOBS n HD P RS HNB HOBS
A. spatulispina 0A 53 0.779 0.0038 3.1 0.343 0.328 45 0.833 0.0042 3.5 0.457 0.469
0B 42 0.672 0.0039 3.1 0.458 0.381 22 0.833 0.0047 2.8 0.415 0.464
A. brachiata 10A 33 0.917 0.0056 3.5 0.480 0.454 48 0.950 0.0047 3.0 0.488 0.492
10B 57 0.911 0.0040 3.3 0.545 0.428 31 0.890 0.0037 3.6 0.538 0.485
30A 36 0.942 0.0049 3.0 0.492 0.375 52 0.988 0.0070 3.4 0.527 0.403
30B 51 0.892 0.0069 2.8 0.432 0.349 59 0.940 0.0048 3.2 0.483 0.381
Mitochondrial DNA diversity values are represented in italics (HD, haplotype diversity; p, nucleotide diversity). Indices from allozyme data are
represented by RS (allelic richness based on a diploid number of 22 individuals), HNB, (unbiased expected heterozygosity, Nei 1987) and HO
(observed heterozygosity)
Table 5 Estimates of the fixation index FIS for each Acrocnida species, within each station (J refers to June; S refers to September)
A. spatulispina A. brachiata
OAJ OAS 0BJ 0BS 10AJ 10AS 10BJ 10BS 30AJ 30AS 30BJ 30BS
HK -0.01 -0.070 -0.159 -0.066 -0.019 -0.35 -0.165 0.079 0.011 -0.144 0.186 0.009
PGM -0.049 0.104 -0.091 -0.027 0.128 -0.016 0.282*** 0.484*** 0.305* 0.004 0.221* 0.267*
PGI -0.097 -0.313 0.052 -0.400 0.314* 0.076 0.092 -0.161 0.124 -0.079 -0.120 0.06
ME 0.633*** 0.024 0.814*** -0.167 0.364*** 0.192*** 0.514*** 0.166*** 0.341*** 0.279*** 0.664*** 0.542***
MPI -0.021 0.113 0.142* 0.031* 0.426*** 0.200*** 0.308*** 0.45*** 0.309*** 0.542*** 0.198*** 0.467***
Multilocusaverage
0.043 -0.027 0.171*** -0.119 0.055 -0.008 0.239*** 0.238*** 0.217*** 0.101*** 0.194*** 0.213***
Linkagedisequilibrium
PGM-MEME-
PGIME-MPI HK-MPI HK-ME
Tests of significance were performed with GENEPOP 3.4 (Raymond and Rousset 1995); *P \ 0.05; ***P \ 0.001. Significant linkage dis-
equilibria estimated between pairs of loci at each sampling station are also indicated
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30A in September. This was associated with the common
haplotype HS1 comprising the biggest proportion of hap-
lotypes in 30A when compared to 10B.
In terms of allozyme diversity, both expected (HNB) and
observed (HO) heterozygosities were higher in A. brachiata
than in A. spatulispina (Table 3) although there were no
differences in allelic richness (RS). In contrast to the mito-
chondrial dataset, clear differences in allozyme frequencies
between sampling dates were observed at nearly all stations.
For example, at four subtidal stations, an increase in Pgi-108
between June and September occurred concomitantly with
an increase in Me-100 and a decrease in Mpi-100. These
temporal variations in allele frequencies corresponded to
significant monolocus P-values in the Waples’ (1989) test
(Fig. 2b) and with significant temporal genetic differentia-
tion observed within the two stations situated at 10 m depth
(10A and 10B). Highly significant temporal changes also
occurred at station 30B but not at station 30A (Table 4d),
suggesting a high degree of self-recruitment and a limited
degree of hybridization at this site. Globally, genetic dif-
ferentiation was more pronounced in June between the two
stations of a same transect (10A vs. 30A or 10B vs. 30B),
than in September between stations of the same bathymetric
level (10A vs. 10B or 30A vs. 30B). Nevertheless, spatial
differentiation between subtidal stations in June and in
September was always highly significant. Overall, depar-
tures from Hardy–Weinberg proportions were highly
significant in both June and September (see FIS values in
Table 5), with heterozygote deficiencies observed at all
stations except for station 10A. In relation to the observed
departures from Hardy–Weinberg equilibrium at the Me and
Mpi loci, significant genotypic disequilibrium between the
two loci was also apparent.
Discussion
Spatial isolation and spawning asynchrony as
pre-zygotic mechanisms limiting local hybridization
On the basis of hybridization laboratory experiments and in
situ observations, Mallet (2005) showed a linear negative
relationship between species divergence (and so the time
since divergence) and cross-fertilization. Similarly, hybrid
viability also decreases as a function of divergence (Bolnick
and Near 2005). The occurrence of hybridization at a fre-
quency of 2.6% between the two spatially segregated and
highly divergent Acrocnida species (DAVG-COI = 19.6%;
hALLOZYMES = 0.22) clearly indicates incomplete repro-
ductive isolation among natural populations. The distribu-
tion of the hybridization index is clearly bimodal with rare
hybrids and predominating parental forms. While bimo-
dality is supposed to be associated with assortative mating
or preferential fertilization (Jiggins and Mallet 2000)
experimental trials established to test for preferential
assortative mating and hybrid viability of Acrocnida failed
thus leaving a number of unanswered questions.
The two Acrocnida species largely segregate with depth,
with an abrupt transition at low tidal levels. The temporal
stability of this bathymetric segregation may suggest that
strong selective mechanisms associated with depth operate.
While selection against migrants across the low tide
boundary may occur through habitat-specific differential
mortality, the short dispersal phase of pelagic larvae
(around 4 days) and the gregarious behaviour of the species
both act to reduce larval settlement or juvenile/adult dis-
persal in opposite habitats. Studies have shown the direct
(Schmidt and Rand 2001) and indirect (Cruz et al. 2004)
effects of selection by depth on the spatial restriction of
genotypes. In addition, the fact that individuals of both
species are strongly restricted to different bathymetric
levels drastically reduces further the probability of cross-
fertilization. Even in the extreme case of long-distance
fertilization of the sea-star Acanthaster planci, success
rates drops abruptly 40 meters from the source (Babcock
et al. 1994). Acrocnida sp. is not a long distance fertilizer
and the rapid dilution of gametes may be significantly
increased in the intertidal zone, compared to the subtidal
(Denny and Shibata 1989). Even given full gametic com-
patibility and long-distance dispersal, taxa that spawn in
allopatry are obviously less likely to cross-fertilise (Lessios
1984; Byrne et al. 1994). Together with bathymetric seg-
regation and the short larval dispersal phase, marine cur-
rents—e.g. strong outward currents at the entrance of the
study area (station 30A; Blanchet et al. 2004)—may also
act to limit the meeting of gametes between neighbouring
demes and favour self recruitment processes.
Hybridization is also physically limited by temporal iso-
lation linked to reproductive asynchrony, with a 2-weeks
delay in spawning activity between species. Spawning
asynchrony is a characteristic of many marine sibling species
living in sympatry (Knowlton 1993). This is an evolutionary
mechanism which, when gametic, habitat and/or behavioural
isolation are incomplete, may lead to parapatric and sym-
patric forms of speciation. Differences in gamete maturation
between subtidal and intertidal samples of what was at time
thought to represent only A. brachiata were noticed 20 years
ago by Bourgoin et al. (1991) but were only viewed as the
result of differences in the thermal regime affecting indi-
viduals of the same population. It is now clear that this
spawning shift actually corresponds to the existence of two
morphologically distinct species. The earlier spawning per-
iod demonstrated for the subtidal species may reflect the
more stable conditions found at this bathymetric level,
compared to the intertidal zone where stress linked to
emersion is high. Spawning in temperate waters is highly
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dependent on seasonal variations of temperature and nutri-
ents. Such parameters greatly vary with latitude but also with
depth where environmental conditions are buffered com-
pared to the intertidal zone. This hypothesis was emitted by
Nichols and Barker (1984) to explain a similar spawning
asynchrony between intertidal and subtidal populations of
Asterias rubens in the English Channel. A further explana-
tion is based on the gregariousness of externally fertilising
species: the more abundant the individuals are, the more they
will interact and the earlier spawning may take place relative
to the case where individuals are less abundant. This could
help explain the earlier spawning event observed in the
subtidal area where density is at least ten times more
important (Bourgoin 1987; D. Muths, personal observation).
The timing of spawning activity may also be a heritable trait
since demic populations are often composed of a mixture of
individuals that reproduce at different times, and this can be
essential to the stability of the whole meta-population.
Genetic exchanges within a given population (or deme) may,
however, decrease with increasing differences in reproduc-
tive timing, thus generating a process of Isolation-By-Time
(IBT) and adaptation (Hendry and Day 2005). Environ-
mental determinism and heritability in reproductive timing
are, however, not mutually exclusive explanations. Levitan
et al. (2004) showed that a shift of only 2 h in the spawning of
two coral species was sufficient to greatly reduce fertilization
success. The spawning asynchrony that characterizes
Acrocnida species is surely a common feature among other
sister species with similar bathymetric restrictions, for
example among intertidal and subtidal lineages of the
polychaete tubeworm Owenia fusiformis (Jolly et al. 2006).
Our results indicate that the combined effect of spatial
ecological constraints and temporal spawning asynchrony
act as a strong mechanism of pre-zygotic isolation greatly
reducing the likelihood of hybridization between lineages.
Nevertheless, such pre-zygotic barriers are incomplete to
offset hybridization.
Limited role of post-zygotic mechanisms in preventing
hybridization
The presence of even low levels of hybridization among the
two species of Acrocnida sp. reinforces the idea that hybrid
zones can persist over long periods of time through a balance
between dispersal of parental types and selection against
their hybrids (Harrison 1993). In our case, results indicate
that the average age between lineages (over 3.5 million years
ago if we assume an average constant mutation rate; Muths
et al. 2006) is still too short relative to the accumulation of
significant post-zygotic incompatibilities. Indeed, this is
demonstrated by the existence of different levels of intro-
gression which indicates that hybrids might not be sterile or
poorly adapted to local reproduction. On the contrary, the
fact that fewer hybrids were sampled in September compared
to June 2005, as well as the decrease at station 0A between
June and September of one diagnostic allele of A. brachiata
(Hk-100), might also indicate selective mortality operating
against Acrocnida sp. hybrids. Thus, some of our data indi-
cates that post-zygotic isolating mechanisms are acting to
reinforce pre-zygotic ones. Due to our restricted sampling
scheme, we cannot rule out the alternative explanation of
migration by juvenile hybrids. These results emphasise the
idea that multiple pre-zygotic and post-zygotic factors are
needed to create a definite barrier to genome re-homogeni-
zation, especially among closely related species living in
sympatry (Bierne et al. 2002).
There are a number of ways by which post-zygotic
processes may have affected small scale patterns of genetic
differentiation observed within each species, and which
could explain the transient nature of genetic structure
between June and September. Whereas hybridization
events tend to homogenize genetic signature between
species, it also creates some spatio-temporal structure at
the within-species level due to different levels of intro-
gression and heterogeneity of hybrid distribution. Conse-
quently, post-zygotic processes such as hybrid mortalities
which should homogenize hybrid repartition will decrease
genetic differentiation between two stations of a same
species but will also generate differentiation between two
temporal samples of the same station. But, keeping in mind
the low proportion of hybrids, this counter-selection, alone,
can definitively not explain all the within-species spatial
genetic structure observed in Douarnenez Bay.
Migration dynamics is shaping the within-species
genetic structure differently according to habitat
In June, a pronounced genetic structure was observed
between populations of both species, with all pairwise values
of genetic differentiation being significant. This may indi-
cate that gene flow is reduced even between neighbouring
demes, which fit well with expectations based on a very
short-larval phase (Muths et al. 2006). This could also be
caused by strong selective mortalities associated with
increased intra/inter-specific competition during the first few
months of the benthic juvenile life (Gosselin and Qian 1997).
In September, the extent and significance levels of
spatial differentiation in both species was far from the
structure observed in June. This is especially true for the
two intertidal stations where A. spatulispina was sampled
and for which we observed highly significant temporal
changes, followed by spatial genetic homogeneity. Tem-
poral genetic changes implicating a reduction in spatial
genetic structure was also observed for A. brachiata,
although generally to a much lesser extent, with temporal
differentiation only marginally significant (10A and 10B) or
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not significant at all (30A). Significant values of the
Waples’ (1989) test suggest that temporal variations in
allele frequencies are greater than expected under the
influence of drift alone (sampling or genetic drift). The
differentiation observed between June and September is
likely due to allele frequency changes at one or more loci, in
relation to migration and selective mortality. While the
increase of Pgi-108 among A. brachiata samples at subtidal
stations could reflect selective effects, the appearance of
Pgi-90 at station 30A or Hk-110 at three of the four subtidal
stations in September clearly implicate migration processes.
Among A. spatulispina, these migration processes can be
illustrated in September by the appearance of high propor-
tions of new haplotypes (HI5 & HI4), spatial genetic
homogenization at intertidal stations and an increase in both
mitochondrial and nuclear diversities at station 0A.
Considering migrations in Acrocnida species, one
peculiar feature of our data is that all the sampled brittle-
stars were characterised as juveniles or adults (all more than
7 mm), and no newly recruited individuals were found.
Therefore, migration events of both juvenile and adult
stages may be considered as a feasible alternative explain-
ing the spatio-temporal genetic structure in Dournenez Bay.
The migratory behaviour of adult brittle-stars, including
A. brachiata, has already been suggested to occur during
summer periods in the Bristol Channel (Tyler and Banner
1977). In this case, migration could either be due to rafting
(Hendler and Miller 1991; Hendler et al. 1999) or active
swimming with the tide, a behaviour also noticed for other
benthic invertebrates (Farke and Berghuis 1979; Guillou
1980; Goodacre 2006). Migration could also be brought
about by passive displacements caused, for example, by
high rates of sediment re-suspension as a result of storm
activity. This has frequently been observed for soft sedi-
ment marine invertebrates (Tamaki 1987; Zuhlke and Reise
1994; Grant et al. 1997) and in Dournenez Bay itself
(Pectinaria koreni; Jolly and Gentil, personal observation).
All the above affect population stability, and which might
explain, not only the strong temporal changes in allele
frequencies and the spatial genetic homogenization of
intertidal A. spatulispina samples, but also the pronounced
and more stable spatial genetic structure observed among
subtidal A. brachiata samples.
For both species, the homogenizing effect on allele
frequencies observed within and between stations over the
summer period is best explained by active migratory events
(juvenile, adults) in conjunction with hybrid mortalities.
On the contrary, even limited hybridization events during
the spawning season coupled to strong adult mortalities
following reproduction (reported by Bourgoin et al. 1991)
tend to generate local genetic structure within a species as
seen in June. Both selection and migration therefore play
an important role in the genetic population structure of
each lineage, at least at this small spatial scale and over this
short time frame. As these two evolutionary forces may act
synergistically but differently at each locality within the
embayment (whether subtidal or intertidal), larger scale
patterns such as historical isolation by distance may easily
be masked.
This study illustrates the fact that incomplete repro-
ductive isolation may occur between highly divergent
species and that local hybridization together with selective
pressures may affect population structure. It also shows
how reproductive isolation is maintained during the for-
mation of species, or after secondary contact, through a
combination of asynchronous population dynamics and
local selective constraints. Pre-zygotic processes such as
ecological preferences, which may be caused by phyloge-
netic niche conservatism (Wiens and Donoghue 2004), and
spawning asynchrony are the most likely pre-zygotic bar-
riers to interspecific matings contributing to reproductive
isolation in A. brachiata. Hybrid inviability does not seem
to be a strong contributing post-zygotic factor in sympatric/
parapatric speciation via reproductive isolation. Infertility
of the F1 & F2 generation should however be tested
experimentally. In addressing the particular environmental
conditions favouring the spatial segregation of ecotypes
and genotypes, new in situ post-larval data collection and
eco-physiological experiments (such as in Edmands and
Deimler 2004; Gardner and Thompson 2001) would truly
be an interesting complement to the present study.
Acknowledgments We are very grateful to people who helped us in
the collection of samples, particularly to the crews of the N/O ‘‘Cotes
de la Manche’’ and ‘‘Cotes d’Aquitaine’’. Many thanks also to the
divers of the ‘‘Station Biologique de Roscoff’’, Caroline Broudin
and to Yvan Lebras. This work was funded by the ‘‘PNEC-AT’’
(Programme National sur l’Environnement Cotier), the European
network of excellence ‘‘Marbef’’ (Marine Biodiversity and Ecosystem
Functioning) and supported by a PhD grant from the French Ministry
of Research.
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