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Mitochondrial DNA and Color Pattern Variation in Three Western Atlantic Halichoeres (Labridae), with the Revalidation of Two Species

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Genetic surveys of widely distributed marine species often find previously undetected biodiversity. In the present study, populations of three species of Halichoeres were sampled across their entire geographical ranges: Halichoeres cyanocephalus and Halichoeres maculipinna were sampled on both sides of the Amazon freshwater outflow, the main biogeographic barrier in the tropical western Atlantic; and Halichoeres garnoti was sampled in the Caribbean and Bermuda. Genetic divergences between populations separated by the Amazon ranged from 2.3% in H. cyanocephalus to 6.5% in H. maculipinna. There is inconsistency between color differences and genetic partitions in the species surveyed. The color differences between populations of H. cyanocephalus and H. maculipinna correspond to deep genetic partitions at the cytochrome b locus. However, genetic similarity at this same locus was observed between populations of H. garnoti with striking color differences. Based on the combination of the observed genetic differences with diagnostic color differences, the Brazilian species Halichoeres dimidiatus (Agassiz) and Halichoeres penrosei Starks, 1913 are revalidated. In addition, a neotype is designated to H. cyanocephalus (Bloch, 1791), to clarify its taxonomic status and type locality. All species analyzed have a similar larval dispersal potential, but varying degrees of genetic divergences were observed, indicating that benthic stage ecology may also play a role in speciation in this group.
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2004 by the American Society of Ichthyologists and Herpetologists
Copeia, 2004(4), pp. 770–782
Mitochondrial DNA and Color Pattern Variation in Three Western
Atlantic Halichoeres (Labridae), with the Revalidation of Two Species
L
UIZ
A. R
OCHA
Genetic surveys of widely distributed marine species often find previously unde-
tected biodiversity. In the present study, populations of three species of Halichoeres
were sampled across their entire geographical ranges: Halichoeres cyanocephalus and
Halichoeres maculipinna were sampled on both sides of the Amazon freshwater out-
flow, the main biogeographic barrier in the tropical western Atlantic; and Halichoeres
garnoti was sampled in the Caribbean and Bermuda. Genetic divergences between
populations separated by the Amazon ranged from 2.3% in H. cyanocephalus to 6.5%
in H. maculipinna. There is inconsistency between color differences and genetic
partitions in the species surveyed. The color differences between populations of H.
cyanocephalus and H. maculipinna correspond to deep genetic partitions at the cy-
tochrome b locus. However, genetic similarity at this same locus was observed be-
tween populations of H. garnoti with striking color differences. Based on the com-
bination of the observed genetic differences with diagnostic color differences, the
Brazilian species Halichoeres dimidiatus (Agassiz) and Halichoeres penrosei Starks,
1913 are revalidated. In addition, a neotype is designated to H. cyanocephalus (Bloch,
1791), to clarify its taxonomic status and type locality. All species analyzed have a
similar larval dispersal potential, but varying degrees of genetic divergences were
observed, indicating that benthic stage ecology may also play a role in speciation in
this group.
T
HE presence of potentially widely dispers-
ing planktonic larva in most marine fishes
has led to the assumption that such species are
composed of genetically homogeneous popula-
tions (Warner, 1997). However, recent studies
on larval behavior (Leis and McCormick, 2002)
and oceanographic processes (Cowen, 2002) in-
dicate that larvae often disperse far less than
their potential. Moreover, habitat selection by
larvae can also overcome the effects of long-dis-
tance dispersal and give rise to genetic differ-
ences in geographically close populations (Bier-
ne et al., 2003). Consequently, genetic studies
of widely distributed taxa often reveal the pres-
ence of previously overlooked species (Knowl-
ton, 2000).
Early genetic surveys within the Caribbean re-
gion found no evidence of cryptic speciation in
reef fishes (Shulman and Bermingham, 1995).
However, when broader geographic areas were
sampled, analyses of DNA variation demonstrat-
ed the presence of deeply divergent evolution-
ary partitions in several species, such as bone-
fishes (Colborn et al., 2001), blennies (Muss et
al., 2001), surgeonfishes (Rocha et al., 2002),
groupers (Carlin et al., 2003), and wrasses (Ro-
cha, 2003a). Some of these genetic divergences
are accompanied by slight color differences.
In reef fish taxonomy, color pattern is consis-
tently used as a useful diagnostic character.
When color differences are observed between
populations that also show slight morphological
differences, those populations are usually ele-
vated to specific status (Randall, 1998). Howev-
er, color alone is rarely used as a character to
define species, especially in groups with highly
variable intraspecific color patterns such as
wrasses (Labridae). Despite the presence of
bright color patterns and their wide variation
observed in reef fishes, little is known about its
evolutionary significance (McMillan et al.,
1999). Sexual selection related to coloration ap-
pears to be present in damselfishes (Pomacen-
tridae; Thresher and Moyer, 1983), but no cor-
relation between mating success and color pat-
tern was observed in the blue-head wrasse (La-
bridae; Warner and Schultz, 1992). In closely
related species, coloration has been proposed
to be useful in mate recognition. The sharpnose
pufferfishes are an example of a group with lit-
tle or no diagnostic external morphological
characters, where color has been proposed as
important in speciation and is routinely used as
a species defining character (Allen and Randall,
1977; Moura and Castro, 2002).
Wrasses of the genus Halichoeres in the west-
ern Atlantic provide an excellent system to ex-
amine the relationship between genetic struc-
ture and color differentiation. The populations
surveyed in this study are present on both sides
of recognized biogeographic barriers, have a
similar dispersal potential (pelagic larval phase
771ROCHA—MITOCHONDRIAL DNA VARIATION IN HALICHOERES
Fig. 1. Tropical western Atlantic. Numbers repre-
sent sampled locations: 1. Bermuda; 2. Bahamas; 3.
Florida Keys; 4. Belize; 5. St. Croix; 6. Venezuela; 7.
northeast Brazil; 8. southeast Brazil; 9. Trindade Is-
land. Solid arrows indicate direction of mean surface
oceanic currents; broken lines indicate subsurface
currents.
of 25–30 days; Sponaugle and Cowen, 1997;
Wellington and Robertson, 2001) and exhibit
slight color differences. Populations of Halicho-
eres garnoti in the Caribbean and Bermuda are
separated by at least 1400 km of open-ocean
(Smith-Vaniz et al., 1999), and populations of
Halichoeres cyanocephalus and Halichoeres maculi-
pinna in Brazil and the Caribbean are separated
by the Amazon barrier ( Joyeux et al., 2001; Ro-
cha, 2003b). These populations have been con-
sidered to be the same species, but they show
consistent color differences in three instances:
(1) the juveniles of H. cyanocephalus in Brazil
lack a blue spot on the midventral portion of
the soft dorsal fin, which is present on juveniles
of the Caribbean population; (2) terminal-
phase males of H. garnoti at Bermuda have a red
band on the upper posterior portion of the
body, whereas males from the Caribbean have a
black band at the same place; (3) the upper
body of individuals from the Brazilian popula-
tions of H. maculipinna is usually brownish-pink,
whereas individuals from the Caribbean have a
yellowish-green upper body.
Samples of the above-mentioned species were
collected across their entire geographical range
in the tropical western Atlantic, and an analysis
of mitochondrial DNA sequences was carried
out aiming to assess the following questions: (1)
Does genetic differentiation parallel the ob-
served patterns of color differentiation in west-
ern Atlantic Halichoeres? (2) Do biogeographic
barriers (the Amazon freshwater outflow and
vast open-ocean distances) equally affect species
with similar dispersal potential?
M
ATERIALS AND
M
ETHODS
Specimens were collected with pole spears or
hand nets while scuba diving or snorkeling in
Bermuda, the Bahamas, Florida, Belize, St.
Croix (U.S. Virgin Islands), Venezuela, Paraı´ba
(northeastern Brazil), Espı´rito Santo (south-
eastern Brazil) and Trindade Island (Fig. 1) be-
tween 1997 and 2002. Tissue (muscle and/or
gill) was stored in a saturated salt-DMSO buffer
(Amos and Hoelzel, 1991).
Total genomic DNA was extracted using QIA-
GEN DNeasy extraction kits following the man-
ufacturer’s protocol. Extracted DNA was frozen
in TE buffer (10 mM Tris-HCl, pH 7.5 and 1
mM EDTA, pH 8.0, diluted in water) and ar-
chived at
2
20 C. Primer names indicate the
DNA strand (H
5
heavy and L
5
light strand)
and the position of the 3
9
end of the oligonu-
cleotide primer relative to the human mito-
chondrial DNA sequence. A fragment of ap-
proximately 800 base pairs of the mtDNA cyto-
chrome b gene was amplified with the primers
L14725 (5
9
GTG ACT TGA AAA ACC ACC GTT
G3
9
) and H15573 (5
9
AAT AGG AAG TAT CAT
TCG GGT TTG ATG 3
9
; Meyer, 1993). Based on
initial sequences, the internal primers L14768
(5
9
ACC CAC CCA CTC CTT AAA ATC 3
9
), and
H15496 (5
9
TTG GAG ACC CAG ATA ATT TCA
C3
9
) were designed and worked consistently
among Halichoeres species, yielding a product of
690–709 base pairs.
Thermal cycling in polymerase chain reac-
tions (PCR) consisted of an initial denaturing
step at 94 C for 1 min 20 sec, then 35 cycles of
amplification (40 sec of denaturation at 94 C,
30 sec of annealing at 52 C, and 55 sec of ex-
tension at 72 C), and a final extension of 2 min,
30 sec at 72 C. Excess primers were removed by
incubation of PCR products with exonuclease I
and shrimp alkaline phosphatase (USB Corp.,
Cleveland OH).
Sequencing reactions with fluorescently la-
beled dideoxy terminators (BigDye, Applied
Biosystems, Inc., Foster City, CA) were per-
formed according to manufacturer’s recom-
mendations and analyzed with an ABI 377 au-
tomated sequencer (Applied Biosystems, Inc.,
Foster City, CA). All samples were sequenced in
the forward direction (with L14725 or L14768
primers), and rare or questionable haplotypes
were sequenced in both directions to ensure ac-
curacy of nucleotide designations. Haplotypes
of all species were deposited at GenBank (see
Material Examined section).
772 COPEIA, 2004, NO. 4
Fig. 2. Phylogenetic tree of Halichoeres cyanocephal-
us (Belize) and Halichoeres dimidiatus (Brazil) unique
haplotypes. Neighbor-joining bootstrap support (
.
50%) indicated on nodes, maximum-parsimony sup-
port below nodes. Branch lengths are according to
indicated scale; the branch leading to the outgroup
(Halichoeres garnoti) was reduced by 50%.
Sequences were aligned and edited with Se-
quencher version 3.0 (Gene Codes Corp., Ann
Arbor, MI). The computer program MODEL-
TEST version 3.06 (Posada and Crandall, 1998)
was used to determine the substitution model
and the gamma distribution shape parameter
that best fit the data through hierarchical like-
lihood ratio tests (hLRTs). The HKY (Hasegawa
et al., 1985) substitution model was chosen for
all datasets and the gamma distribution shape
parameter varied from 0 in H. cyanocephalus to
0.1 in H. maculipinna to 0.4 in H. garnoti. The
analyses were also run using the Tamura-Nei
substitution model (Tamura and Nei, 1983)
with no significant changes in tree topology. Re-
lationships between unique haplotypes were re-
constructed based on starting trees calculated
using the neighbor-joining method (Nei, 1987)
and further searched by 10
7
tree bisection and
reconnection (TBR) iterations under the mini-
mum evolution criterion with the software
PAUP* version 4.0b10 (D. L. Swofford, Sinauer,
Sunderland, MA, 2002, unpubl.). Additionally,
maximum parsimony analyses were performed
on datasets with deep phylogenetic breaks. To-
pological confidence was evaluated with 1000
bootstrap replicates (Felsenstein, 1985). Equal
weighting of all three codon positions was used.
Population structure and gene flow were as-
sessed with the program Arlequin v2.0 (S.
Schneider, D. Roessli, and L. Excoffier, Univer-
sity of Geneva, Switzerland, 2000, unpubl.),
which generated F
ST
-values (a molecular analog
of F
ST
that takes into consideration sequence di-
vergence among haplotypes). Genetic variation
is described with nucleotide diversity (
p
, equa-
tion 10.19; Nei, 1987) and haplotype diversity
(h, equation 8.5; Nei, 1987) within each loca-
tion.
In addition to the genetic analysis, morpho-
logical comparisons were also carried out.
Counts and measurements follow Randall and
Lobel (2003). Measurements were taken with a
digital caliper and recorded to the nearest tenth
millimeter. Unless otherwise stated, institutional
abbreviations follow Leviton et al. (1985). Spec-
imens from the following museums were ex-
amined: MBML (Museu de Biologia Melo Lei-
ta˜o, Espı´rito Santo, Brazil), MCZ, MZUSP, SU,
UF, UFES (Colec¸a˜o Ictiolo´gica, Universidade
Federal do Espı´rito Santo, Brazil), UFPB (Co-
lec¸a˜o Ictiolo´gica, Universidade Federal da Pa-
raı´ba, Brazil), USNM and ZUEC (Museu de His-
toria Natural, Universidade Estadual de Cam-
pinas, Brazil).
R
ESULTS
Halichoeres cyanocephalus.—A 701 bp fragment
from the cytochrome b gene was analyzed from
17 individuals. A total of 26 polymorphic sites
distributed among 10 haplotypes were identi-
fied. Mean nucleotide frequencies were A
5
0.22, C
5
0.31, G
5
0.16, T
5
0.31. The tran-
sition:transversion ratio was 5.5:1. The phylo-
genetic analysis (Fig. 2) assigned the haplotypes
of H. cyanocephalus into two lineages (Brazil and
Caribbean). Pairwise distances within lineages
ranged from 1.17–2.83 nucleotide substitutions
(d
5
0.002–0.004). Although sample sizes are
low, Brazilian and Caribbean populations are
separated by at least 16 mutations (d
5
0.023)
and the F
ST
between Brazil and Belize was 0.91
(P
,
0.01). No morphological difference was
detected between the lineages; however, a slight
color difference is present (Fig. 5C–D).
Halichoeres garnoti.—A 704 bp fragment from
the cytochrome b gene was analyzed from 116
individuals. A total of 66 polymorphic sites were
distributed among 55 haplotypes. Mean nucle-
otide frequencies were A
5
0.22, C
5
0.30, G
5
0.16, T
5
0.32. The transition:transversion ra-
tio was 10.16:1. No geographic signal was de-
tected in the phylogenetic analysis of H. garnoti
(Fig. 3). Individuals with a red dorsum (indi-
cated by arrows and the letter B in Fig. 3) were
nested within the Caribbean lineage. Genetic
distances among populations ranged from 0.06–
2.45 nucleotide substitutions (d
5
0.001–0.004).
Haplotype diversity was relatively high and over-
all nucleotide diversity (
p
) was low in all pop-
ulations (Table 1). No significant population
structure was observed across the species’ entire
range from Bermuda to Venezuela (Table 2).
773ROCHA—MITOCHONDRIAL DNA VARIATION IN HALICHOERES
Fig. 3. Phylogenetic tree of all (55) Halichoeres gar-
noti unique haplotypes. No geographical signal was
detected in the phylogeny. Arrows indicate haplotypes
shared between Bermuda and one or more Caribbean
location; haplotypes only found in Bermuda are
marked with a B. Bootstrap support (
.
50%) is in-
dicated on nodes. Branch lengths are according to
indicated scale; the branch leading to the outgroup
(Halichoeres poeyi) was reduced by 50%.
Halichoeres maculipinna.—A 691 bp fragment
from the cytochrome b gene was analyzed from
86 individuals. A total of 71 polymorphic sites
distributed among 44 haplotypes were identi-
fied. Mean nucleotide frequencies were A
5
0.22, C
5
0.29, G
5
0.17, T
5
0.32. The tran-
sition:transversion ratio was 5.91:1. The phylo-
genetic analysis (Fig. 4) assigned the haplotypes
of Halichoeres maculipinna into two lineages (Bra-
zil and the North Atlantic) separated by 45.2–
49.0 nucleotide substitutions (d
5
0.065–0.071
sequence divergence). Genetic distances within
lineages ranged from 0.01–2.05 nucleotide sub-
stitutions (d
5
0.001–0.003). Haplotype diversity
was relatively high and overall nucleotide diver-
sity (
p
) was low in all populations of both line-
ages (Table 1).
The two lineages were allopatric, one north-
ern (Florida, Bahamas, St. Croix, Belize, and Ve-
nezuela) and the other southern (coastal Brazil
and Trindade Island), being separated by highly
significant F
ST
-values (F
ST
5
0.958–0.984). No
significant pairwise F
ST
-values were observed
within either lineage (Table 3). No morpholog-
ical difference was detected between the line-
ages; however, a slight color difference is pre-
sent (Fig. 5E–F).
D
ISCUSSION
Halichoeres cyanocephalus.—The genetic diver-
gence (d
5
2.3%) between the Brazilian and
Caribbean populations of H. cyanocephalus (Fig.
2) coincides with a subtle but consistent color
difference: individuals in Belize, Florida, and
the Virgin Islands have the color pattern shown
in Figure 5D, whereas individuals in north and
south Brazil have the pattern shown in Figure
5C. The Amazon is unlikely to be an effective
barrier between Brazilian and Caribbean line-
ages, because the Brazilian lineage occurs over
deep sponge bottoms off Brazil (Rocha et al.,
2000) and French Guiana (Uyeno et al., 1983),
the latter under the Amazon plume.
If not the Amazon barrier, what is causing ge-
netic differentiation between these lineages?
Rocha (2003b) suggests that it may be ecologi-
cal speciation or speciation driven by ‘‘divergent
selection on traits between populations or sub-
populations in contrasting environments’
(Schluter, 2001). Environmental differences be-
tween locations in the Caribbean Sea (charac-
terized by clear waters all year round, relatively
stable environmental conditions, and bottom
sediments largely composed of calcium carbon-
ate) and the Brazilian coast (a typical continen-
tal environment, with terrigenous substrates in-
fluenced by run off from rivers, and high tur-
bidity caused by wind driven suspension of bot-
tom sediments) may generate divergent
selection pressures in the insular versus conti-
nental habitats, potentially promoting ecologi-
cal speciation, even in the presence of small mi-
gration between populations.
Halichoeres garnoti.—As pointed out by Smith-
Vaniz et al. (1999, pl. 12, figs. 78–80), there are
noticeable color differences between Caribbean
and Bermuda populations of this species (Fig.
774 COPEIA, 2004, NO. 4
T
ABLE
1. S
AMPLE
S
IZE
,N
UMBER OF
H
APLOTYPES
,H
APLOTYPE
D
IVERSITY
(h)
AND
N
UCLEOTIDE
D
IVERSITY
(
p
)
OF
THE
P
OPULATIONS
S
URVEYED
.
N Haplotypes h
p
Halichoeres cyanocephalus
Belize
NE Brazil
Total
12
5
17
6
4
10
0.68
6
0.15
0.90
6
0.16
0.002
6
0.001
0.004
6
0.003
Halichoeres garnoti
Bahamas
Belize
Bermuda
Florida Keys
St. Croix
21
21
27
3
23
17
15
20
1
18
0.97
6
0.03
0.95
6
0.03
0.97
6
0.02
0.00
6
0.00
0.98
6
0.02
0.008
6
0.005
0.009
6
0.005
0.008
6
0.004
0.00
6
0.00
0.009
6
0.005
Venezuela
Total
22
117
16
55
0.97
6
0.02 0.009
6
0.005
Halichoeres maculipinna
Bahamas
Belize
NE Brazil
Florida Keys
St. Croix
Trindade
19
19
5
3
18
5
12
12
4
2
9
3
0.90
6
0.06
0.87
6
0.07
0.90
6
0.16
0.67
6
0.31
0.80
6
0.09
0.70
6
0.21
0.003
6
0.002
0.002
6
0.001
0.002
6
0.001
0.001
6
0.001
0.002
6
0.001
0.001
6
0.001
Venezuela
Total
17
86
11
44
0.88
6
0.07 0.003
6
0.002
T
ABLE
2. P
OPULATION PAIRWISE
F
ST FOR
Halichoeres garnoti. No comparisons are significant at P
5
0.05.
Locations 123456
1. Bermuda
2. Florida
3. Bahamas
4. Belize
5. St. Croix
5. Venezuela
0
0.001
2
0.023
0.011
2
0.006
2
0.013
0
0.041
2
0.026
0.141
2
0.078
0
2
0.004
2
0.024
2
0.016
0
2
0.005
0.018
0
2
0.017 0
5A–B). Unlike what occurs in other Halichoeres
species (color differences are matched by fixed
genetic differences in the pair Halichoeres radia-
tus/brasiliensis and the Brazilian and Caribbean
lineages of H. cyanocephalus and H. maculipinna;
Rocha and Rosa, 2001b; Rocha, 2003a) color
differences are not accompanied by fixed ge-
netic differences at the cytochrome b of H. gar-
noti. The population of H. garnoti in Bermuda
shares 12 of its 20 haplotypes with one or more
of the Caribbean locations (Fig. 3). Moreover,
haplotypes endemic to Bermuda are randomly
distributed across the tree on Figure 3.
Three hypothesis may explain the absence of
genetic differentiation despite the presence of
color differences: (1) the population at Ber-
muda is exposed to some environmental con-
dition that causes their color to change phe-
notypically without an underlying genetic basis;
(2) color differences are associated with differ-
ences at loci other than the cytochrome b; (3)
the population at Bermuda is young, possibly
postdating the last glacial maximum, such that
color differences that appeared as a result of
strong selection, drift or founder effect are not
accompanied by fixed genetic differences at the
cytochrome b.
The first two hypotheses remain untested;
however, there is evidence favoring the third.
During the last glacial maximum (25,000 to
15,000 yr B.P.), temperatures at Bermuda were
3–5 C lower than today (Sachs and Lehman,
1999), bringing mean annual temperatures be-
low the 21 C (with much lower temperatures
during the winter) threshold necessary for reef
coral survival and leading to the likely exter-
775ROCHA—MITOCHONDRIAL DNA VARIATION IN HALICHOERES
Fig. 4. Phylogenetic tree of Halichoeres maculipinna
(Caribbean) and Halichoeres penrosei (Brazil) unique
haplotypes. Neighbor-joining bootstrap support (
.
50%) indicated on nodes, maximum-parsimony sup-
port below nodes. Branch lengths are according to
indicated scale; the branch leading to the outgroup
(Halichoeres poeyi) was reduced by 50%.
T
ABLE
3. P
OPULATION PAIRWISE
F
ST FOR
Halichoeres maculipinna. Asterisks indicate significance at P
5
0.05.
Locations 1 2 3 4 5 6 7
1. Florida
2. Bahamas
3. Belize
4. St. Croix
5. Venezuela
6. Coastal Brazil
7. Trindade
0
2
0.101
2
0.075
2
0.105
2
0.100
0.973*
0.984*
0
0.006
0.010
2
0.002
0.958*
0.961*
0
2
0.014
0.013
0.969*
0.972*
0
0.009
0.971*
0.974*
0
0.959*
0.963*
0
0.001 0
mination of most of the tropical reef fish fauna
(Smith-Vaniz et al., 1999). Assuming that H. gar-
noti is a strictly tropical species (it does not oc-
cur in the northern Gulf of Mexico or in any
coastal location north of Florida), it is probable
that the Bermuda population is less than 15,000
years old. Thus, color differences may have a
genetic basis but were not detected in neutral
genes (such as the cytochrome b) because of
insufficient time for lineage sorting (Avise,
2000).
Halichoeres maculipinna.—The pelagic larval du-
ration (PLD) of H. maculipinna (30 days; Spon-
augle and Cowen, 1997) is the longest among
the Atlantic Halichoeres. However, this species
showed the deepest genetic divergence ob-
served in this study (d
5
6.5%) between Brazil-
ian and Caribbean populations, demonstrating
the poor value of PLD as a predictor of genetic
divergence. Despite the deep genetic split be-
tween Brazil and the Caribbean, careful exami-
nation of several individuals of H. maculipinna
from locations at the two regions revealed no
morphological differences. However, slight dif-
ferences in coloration were detected (Fig. 5E–
F).
The divergence observed between Caribbean
and Brazilian lineages of H. maculipinna is the
highest among all species examined. One pos-
sible explanation is that this high divergence is
a result of strict habitat preferences. There are
no field survey data that indicates that H. ma-
culipinna crosses the Amazon barrier; it is a shal-
low water species (20–30 m maximum depth;
Randall and Bo¨hlke, 1965; Humann and De-
loach, 2002) and was not collected under the
Amazon plume (Collette and Ru¨tzler, 1977) or
on deep sponge bottoms off northeastern Brazil
(Rocha et al., 2000). Moreover, H. maculipinna
has the weakest jaw musculature, the smallest
mouth gap and the most specialized diet (fewer
and smaller species of benthic invertebrates
compared to congeners) among all Atlantic
Halichoeres (Randall, 1967; Wainwright, 1988).
As a specialized predator, H. maculipinna may be
more sensitive to habitat differences than the
other more generalist species surveyed here. In
this case, stronger natural selection may lead to
earlier and faster differentiation, possibly gen-
erating the higher observed divergences in this
species.
Taxonomic implications.—The genetic divergence
between the Caribbean and Brazilian popula-
tions observed in this study equals or exceeds
divergences between recognized sister species
pairs of other wrasses (Rocha, 2003a; Bernardi
et al., 2004). In addition, there are diagnostic
color characters that distinguish the Brazilian
populations from their Caribbean counterparts
776 COPEIA, 2004, NO. 4
Fig. 5. Halichoeres garnoti at the Bahamas (A) and Bermuda (B). Halichoeres dimidiatus at northeastern Brazil
(C) and Halichoeres cyanocephalus at Belize (D) Halichoeres penrosei at northeastern Brazil (E) and Halichoeres
maculipinna the Bahamas (F). All photos taken by Luiz Rocha, except 5C (by Gerald Allen) and 5D (by Jack
Randall).
(Fig. 5). Randall (1998) suggested that the im-
portance of diagnostic color characters in reef
fish systematics is dramatically increased when
those characters are observed in combination
with (even minor) diagnostic counts or mea-
surements. Here I propose that this principle
should be extended to genetics: the coinci-
dence of diagnostic genetic and color charac-
ters should warrant elevation of evolutionary
lineages to specific status. Thus, the Brazilian
populations of H. cyanocephalus and H. maculi-
pinna should be considered valid species.
Bloch (1791) gave no type locality for H. cyan-
ocephalus, and no types are known (Randall and
Bo¨hlke, 1965; Eschmeyer, 1998; Paepke, 1999;
Parenti and Randall, 2000). The original de-
scription (Bloch, 1791:140) states [my transla-
tion]: ‘The residence of this fish is for me un-
known. The original drawing is kept in the cab-
inet of Linkeschen (Heinrich Linck).’’ More-
over, the original description is inaccurate and
incomplete because it is based on a single, ap-
parently adult individual. Nonetheless, this
name has been associated with the Caribbean
species since at least the end of the 19th century
( Jordan and Evermann, 1898).
To clarify the taxonomic status and the type
locality of H. cyanocephalus (Bloch, 1791), and
777ROCHA—MITOCHONDRIAL DNA VARIATION IN HALICHOERES
Fig. 6. Neotype of Halichoeres cyanocephalus (UF 224284). Photo by Luiz Rocha.
in accordance with article 75(3) of the Inter-
national Code of Zoological Nomenclature
(ICZN, 1999), I designate UF 224284 (202.2
mm SL) as a neotype. Detailed descriptions of
H. cyanocephalus are available in the scientific lit-
erature (Randall and Bo¨hlke, 1965) and in most
Caribbean reef fish guides (Randall, 1996; Hu-
mann and Deloach, 2002).
Halichoeres cyanocephalus (Bloch, 1791)
Figures 5D, 6
Neotype.—UF 224284, adult from Haulover Cut,
North Miami Beach, Florida, collected on 8 Au-
gust 1967 by W. Zeiller, at a depth between 18
and 27 m. This specimen was chosen because it
has the typical characters described by Randall
and Bo¨hlke (1965) and because it is the best
preserved specimen of this taxon at the Univer-
sity of Florida.
Description of the neotype.—Dorsal IX, 12; anal III,
12; pectoral ii,11; total gill rakers on first arch
19 (seven on the upper limb); lateral-line scales
27 (20
1
2
1
5); anterior lateral-line scales with
three pores; two pairs of enlarged canine teeth
anteriorly in lower jaw, one pair on upper jaw.
Standard length 202.2 mm; total length 227.5
mm; body depth 29.1% SL; caudal peduncle
depth 14.6% SL; head length (HL) 28.3% SL;
snout length 37.8% HL; upper jaw length 22%
HL; eye diameter 14.1% HL; interorbital width
22.3% HL.
Color in alcohol.—Body light brown with a broad
dark brown stripe on upper half, beginning at
pectoral fin and extending into middle of cau-
dal fin; a narrower stripe of lighter brown be-
tween the broad stripe and the dorsal fin. Faint
indication of a dark bar on head, extending up-
ward diagonally from upper posterior half of
eye to upper portion of head. Dorsal fin dark
brown on base, pale on margin; upper base of
pectoral fin with a dark spot.
Distribution, habitat, and ecology.—Caribbean is-
lands, North American coast from Florida to
North Carolina and Central American coast
from Colombia to Belize. Usually solitary, rare
in shallow waters, but juveniles and small adults
frequently observed between 5 and 15 m at Be-
lize; mostly observed at depths over 30 m at the
remaining locations.
The Brazilian species should now be consid-
ered valid as follows.
Halichoeres dimidiatus (Agassiz, in Spix and
Agassiz, 1831)
Figures 5C, 7
This species was originally described as Julis
dimidiatus by Agassiz, in Spix and Agassiz, 1831,
and later placed in the synonymy of Halichoeres
cyanocephalus (Bloch, 1791) by (Jordan and Ev-
ermann, 1898). Agassiz states that several spec-
imens were preserved, but only one (MHNN
563, 153 mm SL) still exists (Kottelat, 1988).
The type locality is given as Atlantic, off Brazil
(Spix and Agassiz, 1831).
Diagnosis.—Dorsal IX, 12 (IX, 11 on remaining
Atlantic Halichoeres, except H. cyanocephalus);
anal III, 12; pectoral 13; total gill rakers 18 to
21; two pairs of enlarged canine teeth anteriorly
in lower jaw. Juveniles and females blue with a
bright yellow region dorsally from mouth to
posterior base of dorsal fin; a single dark spot
on caudal (a small ocellated dark spot at rear
base of dorsal fin in addition to the caudal spot
in H. cyanocephalus). Adults with a broad blue
stripe on upper half of body ending at the be-
ginning of the caudal fin (black and narrowing
as it passes to end of caudal fin in H. cyanoce-
phalus); lower half of body light blue; a diagonal
dark band from eye to nape.
Distribution, habitat, and ecology.—From French
Guyana (Uyeno et al., 1983) to the State of Sa˜o
778 COPEIA, 2004, NO. 4
Fig. 7. Adult Halichoeres dimidiatus, approximately 150 mm SL, Guarapari, southeast Brazil. Photo by Joa˜o
Luiz Gasparini.
Fig. 8. Halichoeres penrosei, approximately 50 mm SL, Guarapari, southeast Brazil. Photo by Joa˜o Luiz Gas-
parini.
Paulo (24
8
S, 46
8
W), in southeastern Brazil (Me-
nezes and Figueiredo, 1985). It is also present
at Fernando de Noronha and Atol das Rocas
(20
8
30
9
S, 29
8
20
9
W) but apparently absent from
the remaining Brazilian oceanic islands of Trin-
dade and St. Paul’s Rocks (Gasparini and Floe-
ter, 2001; Feitoza et al., 2003). Usually observed
solitary; juveniles relatively common in shallow
waters (3–20 m), adults in deeper waters (30–
60 m).
Halichoeres penrosei Starks, 1913
Figures 5E, 8
The Brazilian form of H. maculipinna was de-
scribed as Halichoeres penrosei by Starks (1913);
the 55.7 mm SL holotype (SU 22211) is well
preserved and was collected in tide pools at Na-
tal, northeastern Brazil (5
8
S, 35
8
W), located at
the middle of the range of the species. Digital
photographs and a radiograph of the holotype
are available for download at the California
Academy of Sciences website (http://www.
calacademy.org/research/ichthyology/Types/
index.html).
Diagnosis.—Dorsal IX, 11; anal III, 11; pectoral
14; gill rakers 13–15; one pair of enlarged ca-
nine teeth anteriorly in lower jaw (two pair of
canines on remaining Atlantic Halichoeres except
H. maculipinna). Juveniles and females with
wide black stripe through eye to base of tail,
bordered above by prominent pinkish-brown
line (bright yellow in H. maculipinna). White
scales with orange spots on lower half of body
(no spots on H. maculipinna) Adult males are
primarily green with scales bordered by pink
and a black spot on anterior portion of the dor-
sal fin. Narrow (
,
0.5 mm width) orange stripes
on lower half of head, from mouth to gill open-
ing (stripes are
.
1 mm wide in H. maculipin-
na).
Distribution, habitat, and ecology.—From Parcel
Manuel Luiz (0
8
52
9
S, 44
8
15
9
W; Rocha and Rosa,
2001a) to the State of Sa˜o Paulo (24
8
S, 46
8
W),
in southeastern Brazil (Carvalho-Filho, 1999). It
is present at Trindade Island (20
8
30
9
S, 29
8
20
9
W;
Gasparini and Floeter, 2001), but apparently ab-
sent from the remaining Brazilian oceanic is-
lands (Atol das Rocas, Fernando de Noronha,
779ROCHA—MITOCHONDRIAL DNA VARIATION IN HALICHOERES
and St. Paul’s Rocks; Feitoza et al., 2003). Com-
mon in coral and rocky reef tops to depths of
30 m and often observed solitary or in pairs.
C
ONCLUSIONS
Contrary to expectations of congruent pop-
ulation structure due to similar dispersal poten-
tial (25–30 days; Sponaugle and Cowen, 1997;
Wellington and Robertson, 2001), the genetic
effects of biogeographical barriers varied
among species of Atlantic Halichoeres. Genetic
divergences between Brazil and the North At-
lantic ranged from 2.3% in H. cyanocephalus/H.
dimidiatus to 6.5% in the pair H. maculipinna/
H. penrosei. There is inconsistency between color
differences and genetic partitions in the species
surveyed. The color differences between the
species pairs H. cyanocephalus/H. dimidiatus and
H. maculipinna/H. penrosei correspond to deep
genetic partitions at the cytochrome b gene.
However, genetic similarity at this same gene
was observed between populations of H. garnoti
with striking color differences. Thus, caution
against the use of color differences (when not
supported by genetics and/or morphology) in
the alpha systematics of fishes is herein suggest-
ed, a conclusion also reached by others (Mc-
Millan et al., 1999; Bernardi et al., 2004).
Genetic divergences ranged from 2.3–6.5% in
lineages in Brazil and the Caribbean. A conven-
tional molecular clock of 2% per million years
for the cytochrome b gene (Avise, 2000) sug-
gests that this divergence is between 0.6 and
1.65 millions of years (myr) old, much younger
than the estimated age of the initial connection
of the Amazon with the Atlantic, 10–12 myr old
(Hoorn, 1994; Nittrouer et al., 1996; Costa et
al., 2001). Thus, vicariance alone cannot ex-
plain the observed pattern, and dispersal from
one area to the other after the formation of the
Amazon is probably involved in speciation of
western Atlantic Halichoeres.
The species pair with the highest divergence
(6.5 %, H. maculipinna/H. penrosei) is also the
more reef specialized and the one with the nar-
rowest diet width. Although apparently being
able to cross the Amazon barrier, a deep phy-
logenetic break (2.3 %) between Brazil and the
Caribbean is present in the pair H. cyanocephal-
us/H. dimidiatus. These observations indicate
that divergent environmental conditions (con-
tinental sediment-rich Brazilian waters versus in-
sular, clear Caribbean waters) can be as impor-
tant as vast distances of unsuitable habitat (ei-
ther open ocean waters or the area influenced
by the Amazon) in producing genetic partitions
and that benthic-stage habitat preferences may
be strongly influencing the biogeography of
western Atlantic reef fishes.
M
ATERIAL
E
XAMINED
Voucher catalog numbers followed by num-
ber of specimens and GenBank accession num-
bers in parentheses (when available).
Halichoeres cyanocephalus: Cuba: MCZ 14252 (3,
syntypes of Julis internasalis Poey 1861); Flor-
ida: UF 65506 (1), UF 224284 (1, neotype of
H. cyanocephalus); North Carolina: UF 88359
(2); Belize: UF 126324 (1, AY591376); St.
John, U.S. Virgin Islands: UF 206250 (1); Ja-
maica: UF 229817 (1); Colombia: UF 231301
(1). Sequences without museum voucher:
AY591377–AY591379.
Halichoeres dimidiatus: (all from Brazil); Parcel
Manoel Luiz, Maranha˜o: MZUSP 53066 (2),
UFPB 3890 (1), UFPB 3977 (1); Fernando de
Noronha: MZUSP 14626 (1); Mamanguape,
Paraı´ba: UFPB 4312 (1, AY591380); Cabedelo,
Paraı´ba: UFPB 4325 (2); Joa˜o Pessoa: UFPB
3790 (1), UFPB 4354 (2, AY591381,
AY591382); Recife: MZUSP 47482 (1); Salva-
dor, Bahia: USNM 357718 (1); Guarapari, Es-
´rito Santo: MZUSP 51543 (1), ZUEC 3184
(1), ZUEC 3196 (1), MBML 354 (28); Angra
dos Reis, Rio de Janeiro: MZUSP 66256 (2);
Alcatrazes, Sa˜o Paulo: MZUSP 47146 (1),
USNM 357717 (1), ZUEC 2793 (1). Sequenc-
es without museum voucher: AY591383.
Halichoeres garnoti: Bermuda: UF 119713 (11,
AY591372, AY591374), UF 119725 (1,
AY591375), USNM 348309 (1); Bahamas: UF
13485 (5); Cayman Islands: UF 17620 (3); Co-
lombia: UF 18830 (2); St. John U.S. Virgin
Islands: UF 204900 (2); Belize: UF 209277
(4); Cuba: USNM 343625; Tobago: USNM
318896 (7). Sequences without museum
voucher: AY591366–AY591371.
Halichoeres maculipinna: Bermuda: UF 119714
(2), UF 119731 (9, AY591359); St. John, U.S.
Virgin Islands: UF 203752 (4); Bahamas: UF
206337 (5); Florida Keys: UF 219121 (12); Co-
lombia: UF 223079 (12); Belize: USNM
329838 (1); Tobago: USNM 318864 (4). Se-
quences without museum voucher:
AY591360–AY591365.
Halichoeres penrosei: (all from Brazil); Natal: SU
22211 (1, holotype); Espı´rito Santo: MZUSP
52303 (1), MBML 223 (2), 318(1), 395(1,
AY591354), UFES 037 (1), 208(1); Ceara´:
MZUSP 65172 (1); Arembepe, Bahia: MZUSP
66259 (3); Salvador, Bahia: MZUSP 66268 (10
of 25). Sequences without museum voucher:
AY591355–AY591358.
780 COPEIA, 2004, NO. 4
A
CKNOWLEDGMENTS
I thank my Ph.D. advisor, B. Bowen, for pro-
viding scientific guidance, laboratory space, and
financial support. I also thank A. L. Bass, A. Cas-
tro, H. Choat, B. B. Collette, M. Coura, T. L.
Dias, B. M. Feitoza, C. E. Ferreira, S. R. Floeter,
J. L. Gasparini, Z. Hillis-Starr, S. Karl, B. Luck-
hurst, O. Luiz-Junior, D. Murie, D. Parkyn, B.
Philips, J. Pitt, C. Rocha, D. R. Robertson, I. L.
Rosa, R. S. Rosa, S. Sponaugle, B. Victor, and D.
Weaver for help with sampling and laboratory
work. Discussions with C. Gilbert, S. A. Karl, N.
Knowlton, G. Paulay, and M. Westneat greatly
improved the manuscript. S. Floeter, H. Lessios,
and W. F. Smith-Vaniz critically read the manu-
script. G. Allen, J. L. Gasparini, and J. Randall
provided excellent photographs. Specimen
loans, digital photographs of type specimens,
and access to fish collections for morphological
analyses were made available by G. Burgess, D.
Catania, W. Eschmeyer, K. Hartel, S. Jewett, N.
Menezes, R. Robins, R. Rosa, I. Sazima, A. Var-
andas, and J. Williams. Collection permits were
provided by the Department of Agriculture and
Fisheries of Bermuda (permit 01/12–2001), the
Belize Fisheries Department (permit GEN/FIS/
15/04/2002), the National Park Service at St.
Croix, U.S. Virgin Islands (permit BUIS-2001-
SCI-0004), and Instituto Brasileiro do Meio Am-
biente e dos Recursos Naturais Renova´veis, Bra-
zil (general collecting permit for nonprotected
areas). Fishes were collected following the
guidelines of the University of Florida Institu-
tional Animal Care and Use Committee. This
work was financially supported by CAPES Bra-
zilian Ministry of Education, the Brazilian Navy,
PADI Project Aware, the Smithsonian Tropical
Research Institute, the University of Florida,
and the National Science Foundation through
a grant to B. Bowen (DEB 9727048).
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... The analysis, here, of a larger data set that includes samples from through the Brazilian coast and the Caribbean indicates that this new species is an Islands endemic, whose sister species is B. antilliensis. The genetic distances between those two species (6.3% for COI and 7.4% for cyt b) are comparable to or greater than those found among other congeneric species pairs of gobies (Taylor & Hellberg, 2005;Baldwin et al., 2009;Neilson & Stepien, 2009;Victor, 2013) and reef fishes (Rocha, 2004;Rocha et al., 2008a;DiBattista et al., 2011). In addition to the genetic differences, the insular B. brasiliensis sp. ...
... In some reef fishes and sea urchins, for example, the deep genetic divergences observed among Atlantic biogeographic provinces (d = 2.3-12.7% for cyt b) were attributed to the presence of cryptic species within the Atlantic (Muss et al., 2001;Carlin et al., 2003;Lessios et al., 2003;Rocha, 2004). The divergence values of the most differentiated lineages of B. soporator (median d = 2.7% for COI; median d = 4.1% for cyt b) and B. geminatus (median d = 1.8% for COI; median d = 2.7% for cyt b) are similar to those observed between cryptic species of some reef fishes, but are smaller than those found between sister species in the genus Bathygobius (Table 1). ...
... Several studies have revealed evolutionary partitions that correspond to ecological discontinuities, particularly the Amazon barrier, between tropical reef habitats of Caribbean and Brazilian provinces (Rocha et al., 2002;Rocha, 2003Rocha, , 2004. Underneath the Amazon river plume, there is a reef system of ~9500 km 2 that extends from the Brazil-French Guiana border to Maranhão State, Brazil (Collette & Rützler, 1977;Rocha, 2003;Moura et al., 2016). ...
... Labridae (wrasses) is one of the most diversified groups of marine fish, exhibiting notable diversity in morphological and ecological patterns and evolutionary strategies (Westneat & Alfaro 2005;Cowman et al. 2009). In this family, a large number of new species have been identified in recent decades (Randall 1999a(Randall , 1999bRandall & Cornish 2000;Rocha 2004;Victor 2016). This diversity is accompanied by taxonomic difficulties, which has led to re-evaluation and reordering of several of its species (e.g., Parenti & Randall 2011). ...
... Color patterns are used as a diagnostic taxonomic characteristic in reef fishes, although in some cases have little resolution in groups such as Labridae, in which coloration varies widely (Kishimoto 1974;Rocha 2004). Indeed, many labrids exhibit different color patterns that can vary significantly in the same species (Arnal et al. 2006;Choat et al. 2012). ...
... In the insular regions of the Atlantic, especially the Mid-Atlantic islands, which exhibit population structures, such as in the São Pedro and São Paulo Archipelago and Ascension Island, where B. insularis is reported, populations of different fish species have displayed different chromatic and morphological patterns, generally associated with local adaptive conditions (Bermingham et al. 1997;Molina et al. 2006;Cunha et al. 2014;Souza et al. 2016;Souza, A.S., personal communication). Evolutionary factors such as mutation, genetic drift and natural selection are related to color patterns in labrids (Rocha 2004), and may be particularly effective in isolated insular environments. ...
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Bodianus constitutes a marine fish group of particular interest due to its trophic interactions with reef environments. Knowledge of phylogenetic relationships of this genus have been improved by shared advances of classical and genetic approaches. However, some of its species have yet to be compared regarding its genetic patterns. Morphological variations in body shape and color patterns during the course of ontogenetic development, in addition to recurring sex reversal in species of this genus, make its taxonomy challenging. In the Atlantic Ocean five species have been described: B. scrofa and B. speciosus (Eastern Atlantic), B. rufus (Western Atlantic), B. pulchellus (Western Atlantic and Eastern Atlantic Islands) and B. insularis (Mid-Atlantic islands). The phylogenetic relationships of the last species could not be resolved using genetic analyses. With a very restrict geographic distribution, B. insularis deserves high attention regarding its taxonomic and evolutionary aspects. Here, we use mitochondrial DNA sequences (COI and 16S rRNA) and nuclear analyses (rhodopsin) to assess the genetic divergence of B. insularis in relation to other Atlantic species and clarify its phylogenetic relationships. Bodianus pulchellus and B. insularis were not genetically distinct and are grouped with B. rufus, forming a sister clade of B. speciosus, while B. scrofa is more related to Pacific species. DNA-based and morphological traits are very similar between B. insularis and B. pulchellus, whose most obvious difference is their color pattern. The actual reinterpretation of ecological and biogeographic contexts allows to suggest that B. insularis is most likely a synonym of B. pulchellus, constituting a population enclave of this species.
... As a result, the AOP induces significant physicochemical changes in coastal areas, acting as a barrier to the dispersal of several marine species, particularly reef-associated fishes (Rocha 2003;Luiz et al. 2012). Accordingly, previous comparative genetic studies have identified constraints in gene flow among populations of coastal species, resulting in unique lineages northwards and southwards the AOP barrier (Rocha et al. 2002;Rocha 2003;Robertson et al. 2004;Rocha 2004;Rocha et al. 2005;Ball et al. 2007;Argolo et al. 2018). However, additional reports have shown high gene flow rates among populations separated by the AOP in both pelagic and coastal species, mostly likely favored by long-term larval dispersal or migratory abilities at specific life stages (Rocha et al. 2002;Rocha 2003;Ross Robertson et al. 2006;Rocha and Bowen 2008;Luiz et al. 2012). ...
Article
Traditionally, the apparent paucity of biogeographic barriers in marine environments when compared to terrestrial and freshwater habitats has been associated with high gene flow rates among geographically distant populations. However, physical traits such as tide currents, temperature, and salinity levels may serve as ecological boundaries thus leading to restricted-range phylogeographic patterns (e.g., the outflow plume from the Amazonas-Orinoco rivers between the Caribbean and the Brazilian Province) according to adaptive features of coastal organisms. To assess the degree of cohesiveness among populations and species of marine and estuarine fishes along a latitudinal gradient from Western South Atlantic, we carried out comparative phylogenetic and species delimitation analyses based on Cytochrome C Oxidase I (COI) sequences of 34 fish taxa from the Caribbean and Brazilian coasts. Distinct values of genetic diversity were revealed for both Provinces, ranging from moderate (1 to 2%) to high (≥ 2%) in 11.76% and 20.59% of the analyzed taxa, respectively. Furthermore, a significant genetic differentiation was observed within the nominal taxa Diapterus auratus, Citharichthys spilopterus, and Scorpaena plumieri from the Caribbean, as well as for Haemulon plumierii between the Caribbean and Brazilian Provinces. Such divergence is likely to result from temporal isolation among local populations during sea-level fluctuations during the Pliocene-Pleistocene period. The present findings demonstrate that similar biogeographic boundaries may result in species-specific patterns of genetic connectivity, possibly associated with ecological constraints. Since molecular operational taxonomic units (MOTUs) were identified in certain formal taxa from both Provinces, a systematic revision of these groups is highly recommended. At last, multispecies COI data proved to be helpful to phylogeographic inferences and to support appropriate policies for the conservation of natural resources.
... Several studies of coral reef fishes have revealed concordance among such genetic divergence and morphological divergence (e.g. Rocha 2004;Drew et al. 2008Drew et al. , 2010. ...
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The delineation of species and their evolutionary relationships informs our understanding of biogeography and how regional faunas are assembled. The peripheral geography and local environment of reefs in the subtropical South Pacific likely promotes the allopatric and adaptive divergence of taxa colonising from the tropics; however, the fauna of this region has been relatively understudied. Here, we address the taxonomic and evolutionary relationships among Chrysiptera taxa of the subtropical South Pacific. We use meristic counts, morphometrics and genetic markers to characterise the similarities and differences among four taxa restricted to the South Pacific region that have strikingly different colouration: C. notialis, a taxon restricted to eastern Australia, New Caledonia, Lord Howe Island and Norfolk Island; C. galba, found in the Cook Islands, southern French Polynesia and Pitcairn Islands; and the two disjunct populations of C. rapanui, found in the eastern Pacific around Rapa Nui (Isla de Pascua or Easter Island) and Motu Motiro Hiva (Salas y Gómez) and in the South-western Pacific around Rangitāhua (Kermadec Islands). Our morphometric analysis confirmed that these four taxa, including the two disjunct populations of C. rapanui, are morphologically distinct. However, our genetic analysis revealed that only C. rapanui from Rapa Nui was genetically differentiated, whereas C. rapanui of Rangitāhua, C. galba and C. notialis all shared a common haplotype. Furthermore, none of the taxa could be consistently differentiated based on individual meristic features. Our study reconciles a formerly perplexing and disjunct distribution for C. rapanui, to reveal that C. rapanui is an endemic of Rapa Nui and that the Chrysiptera of French Polynesia, Rangitāhua, and the South-western Pacific have only a very recent history of divergence. Our analyses suggest these subtropical taxa have diverged from a predominantly tropical Chrysiptera genus in morphological features important in determining colonisation success, locomotion and feeding ecology.
... The most similar DNA barcodes (mitochondrial COI gene) are from Pseudanthias ventralis and P. hawaiiensis, with 16.8% and 17.0% uncorrected divergence, respectively. These distances are much higher than average divergences between sister species (Rocha 2004), and even between genera, so it is not surprising that P. hangapiko can be differentiated from these two species by several characters, including the number of anal-fin rays (III, 8 vs. III, 9-10 in P. ventralis and P. hawaiiensis), body depth (3.4-3.8 vs 2.3-3.0), and also by body coloration. ...
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Pseudanthias hangapiko sp. nov. (Teleostei, Serranidae, Anthiadinae) is herein described from three specimens collected from a depth of 83 m in a mesophotic coral ecosystem off Hanga Piko, Rapa Nui (Easter Island), Chile. Pseudanthias hangapiko sp. nov. can be distinguished from its congeners in live coloration and by the following combination of characters: dorsal-fin rays X, 17; anal-fin rays III, 8; pectoral-fin rays 16 (left side of one specimen 17); vertebrae 10+16; scales relatively large, two scales above lateral-line to base of fifth dorsal spine, and 16-17 circumpeduncular scales; gill rakers 11+23; and a slender body, with greatest body depth 3.6 (3.4-3.8) in SL. The most similar DNA barcodes (mitochondrial COI gene) are from Pseudanthias ventralis Randall, 1979 and Pseudanthias hawaiiensis Randall, 1979, with 16.8% and 17.0% uncorrected divergence, respectively. This fish is one of four new species that were documented from a pair of technical dives at a single location in Rapa Nui, emphasizing the high number of undescribed species likely still unknown in mesophotic coral ecosystems, especially in geographically remote locations. Pseudanthias hangapiko sp. nov. adds to the Rapa Nui ichthyofauna, which hosts the second-highest level of endemism in both shallow and deep-water fishes.
... Thorough knowledge of these is needed to understand the taxonomic status of this species, which can then lead to more reliable studies on the biology of the species. As a widespread species, different regions or populations might represent different species, as is frequently being shown for reef fish species (e.g., Rocha 2004;Reece et al. 2010b). ...
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The taxonomic status of the widely distributed Indo-Pacific undulated moray eel, Gymnothorax undulatus, is revised using morphological and genetics features. Ninety-seven specimens previously identified as G. undulatus were examined and their mitochondrial COI and 16S rRNA genes were analysed. The multivariate analysis of eight morphometric characters resulted in separation with little to no overlap among some geographic regions. These groupings explained more than 90% of the total variation, with 86.6% overall classification. Two color morphs were identified, and the South African population was described as new species, Gymnothorax elaineheemstrae n. sp., distinct from G. undulatus in having mottled and faintly reticulated color pattern, 134–136 total vertebrae and further confirmed by the genetic analysis of COI and 16S rRNA with > 0.1 genetic distance. The morphological and genetics results indicate that G. undulatus, previously treated as a single species, consists of more than one species.
... TSA provinces, with the Amazon-Orinoco Plume likely acting as a geographical barrier. This riverine complex has already been recognized by several authors as an influential barrier to the formation of pairs of sister species of shallow-water reef fishes in the Western Tropical Atlantic (Rocha, 2003(Rocha, , 2004Bernal & Rocha, 2011). Thus, using AMOVA with the mtDNA COI dataset we found support for this scenario, with 67.76% of all genetic variance being partitioned between the TNA and Brazilian provinces (NBS ? ...
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The saddled blenny Malacoctenus trian-gulatus is a widely distributed species of cryptoben-thic reef fish that occurs from the Caribbean to southeastern Brazil, including the oceanic islands. Subtle morphological differences have been observed between populations, suggesting some degree of structuring along its distribution, especially between insular and coastal environments. In this study, we conducted phylogeographic analyses of M. triangula-tus based on mitochondrial (cytochrome oxidase I and cytochrome b) and nuclear (rhodopsin) genes, including sequences of M. brunoi, a closely related species endemic to the oceanic islands of southeastern Brazil. Three highly structured lineages were identified within the M. triangulatus complex: one restricted to the Caribbean province probably isolated by the Amazon barrier, and two in the Brazilian province, one in the northeastern oceanic islands (NOI) and another along the coast (including M. brunoi). This result indicates that divergent evolutionary processes have driven the evolution of the saddled benny in the Tropical Southwestern Atlantic: an ancient isolation of the NOI lineage during the Neogene and a recent ecological speciation event in the southeastern oceanic islands, which were connected to the coast during Pleistocene marine regressions. Together, these results provide insights on the evolutionary patterns and oceanographic barriers in the Western Tropical Atlantic.
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Quando se fala em ictiologia no Brasil, a primeira coisa que nos vem mente a bacia do rio Amazonas que, sem d vida, cont m a ictiofauna mais diversificada do mundo. Essa simples lembran a geralmente leva a maioria dos jovens icti logos brasileiros a estudar peixes de gua doce, enquanto a fauna de peixes marinhos recebe aten o relativamente menor. Isso se reflete claramente na escassez de guias de identifica o e cat logos de peixes marinhos do Brasil. Uma das principais caracter sticas da costa norte do Brasil a descarga de volume elevado de gua doce e sedimentos no ambiente marinho, o que contribui para a forma o da mais extensa rea de manguezais do planeta. Esse fator confere regi o condi es ambientais nicas que influenciam fortemente a sua biodiversidade, tanto nas reas costeiras quanto em zonas mais profundas. Entretanto, apesar da fauna de peixes marinhos da costa norte brasileira possuir imensa import ncia biol gica, at ent o a menos conhecida do pa s, embora tenha significativa import ncia na vida das comunidades costeiras e na economia da regi o. Tal lacuna no conhecimento deve-se, possivelmente, ao fato de haver poucas comunidades desenvolvidas ao longo da costa, enquanto as grandes cidades e, por consequ ncia, as universidades e centros de pesquisa, est o localizados no interior e margem de grandes rios. Por m, a costa norte respons vel pela segunda maior produ o pesqueira marinha do Brasil, o que contrasta com a baixa produ o de conhecimento taxon mico e biol gico dos peixes marinhos que comp em a sua fauna, com pequeno n mero de exemplares depositados em cole es zool gicas brasileiras. Embora a atividade pesqueira concentre-se na explora o de reas costeiras, como na pesca da Pescada Amarela e do Gurijuba, a pesca nos recifes mesof ticos da Amaz nia tamb m importante, como na pesca do Pargo, com impacto direto sobre recursos naturais muito pouco conhecidos. Tanto as esp cies end micas, t picas de zonas estuarinas como a Pescada Negra, quanto as esp cies marinhas, encontradas em recifes profundos ao longo da quebra da plataforma continental, compartilham uma hist ria influenciada por mudan as ambientais ocorridas ao longo dos ltimos 11 milh es de anos que moldaram a bacia do rio Amazonas, com efeitos diretos na fauna marinha com h bitos costeiros ou de formas exclusivamente marinhas, conferindo caracter sticas e padr es de distribui o nicos aos peixes marinhos descritos neste livro. O primeiro e maior desafio para a conserva o ambiental a descri o e a cataloga o dos organismos de uma dada regi o. Produzir listas de esp cies e guias de identifica o um fator important ssimo para o conhecimento e manejo da fauna, e fundamental para que medidas de conserva o possam ser implementadas. Permitem, ainda, que recursos naturais possam ser explorados de forma sustent vel e esp cies invasores possam ser monitoradas. Esse conhecimento b sico tamb m contribui para o estabelecimento de diretrizes e limites da explora o de recursos naturais, como o petr leo. Assim, este livro representa ferramentas necess rias para que pescadores amadores e profissionais, cientistas, conservacionistas e curiosos conhe am a diversidade dos peixes marinhos da costa Norte do Brasil. O livro composto por chaves de identifica es, fichas descritivas e ilustra es de todas as esp cies costeiras com registros confirmados para a regi o. Al m disso, cientificamente correto, muito bem organizado e de f cil utiliza o. Sua consulta vai ser indispens vel e extremamente til para o avan o dos esfor os de conserva o da regi o. Parabenizo a todos os autores pela elabora o deste manual, que vai preencher uma das grandes lacunas do conhecimento da ictiofauna marinha brasileira. Luiz A. Rocha Curador e Follett Chair de Ictiologia, California Academy of Sciences
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Two centuries after the famous journey of the German naturalists Spix and Martius through Brazil their travel report has been reviewed with special attention on fishes and the respective localities where these have been collected. New insights could be obtained on the specimens they collected, among those for several species described subsequently by Agassiz as new species. The original type localities could be identified for Prochilodus argenteus, Platystoma corruscans, Doras humboldti, Serrasalmo piranha, Rhinelepis aspera and Pachyurus squamipennis in Januária at the middle São Francisco River, and for Anchoa tricolor, Rhaphiodon vulpinus, Tetragonopterus chalceus, Cathorops spixii, Brycon amazonicus, Sorubim infraoculare, Pinirampus pirinampu and Potamorhina latior opposite Prainha at the lower Amazon. Bulletin of Fish Biology 19: 79-96
Thesis
Este estudo apresentou dados novos e relevantes sobre a geomorfologia, geofísica e biota do ambiente recifal do Seixas/PB, sendo um dos pioneiros nesse ambiente recifal com esse nível de detalhamento. Os estudos geológicos, geofísicos e geoquímicos evidenciaram a existência de compartimentos (praia, plataforma interna e recife), áreas (abrigada, platô recifal e batida) e feições geomorfológicas (canal, planície recifal, crista, frente recifal, pós-recife), indicando que os processos deposicionais do fundo marinho sofreram influência oceanográfica. Não foi possível encontrar a rocha-base de sustentação para a edificação do recife através de três perfurações com profundidade máxima de 250 cm, os resultados das lâminas petrográficas, do difratograma de raios-X analisados e do material coletado nos mergulhos realizados na parede externa do recife demonstraram que o recife do Seixas é uma formação biogênica carbonática coral-algal recente - associada com a evolução da linha de costa, com a elevada sedimentação costeira e agindo em conjunto com a elevação do nível do mar (Período Quaternário Holocênico) -, apoiada no terraço marinho de abrasão sob a planície costeira moldada pela Bacia Sedimentar Paraíba, mais precisamente na Sub-bacia Alhandra e dista aproximadamente 30 km do talude continental nordestino. Atualmente, o recife possui 1,18 km2 de área consolidada com altura máxima de 6 m. A partir de uma base consolidada arenítica ocorreu o assentamento e povoamento de organismos bentônicos, passando por processos de sucessões continuamente. Perfazendo uma área amostral de 225 m², com esforço amostral de 120 h de pesquisas visuais subaquáticas (uso de transectos e fotoquadrados) foi possível mapear as comunidades macroalgais, coralíneas e íctica e verificar que as variáveis ambientais profundidade e granulometria exercem influência na estruturação das comunidades. Em uma cobertura dominada por macroalgas (68,99%), corais, hidrocorais e zoantídeos (7,62%), estruturas calcárias - rodolitos (9,73%), sedimento não-consolidado (11,89%) e sedimento consolidado (1,77%), foram identificados 1435 peixes recifais, representados pelas famílias Haemulidae (696 indivíduos), Labridae-Scarinae (272 indivíduos), Pomacentridae (248 indivíduos), Acanthuridae (108 indivíduos) e em menor número de indivíduos, as famílias Epinephelidae, Mullidae, Sciaenidae, Holocentridae e Gobiidae. Como análise geral, a relação entre as áreas Abrigada e Platô e entre as áreas Batida e Platô, aponta a área Platô como um ambiente de ecótono. A nível de endemismo, quatro famílias coralíneas da ordem Escleractinia e oito espécies da ictiofauna são endêmicas da Província Biogeográfica Atlântico Sul, corroborando com a caracterização geral desta província (baixa diversidade com alto grau de endemismo, sobrevivendo em águas turvas). Através de oficinas e mapas conceituais construídos pelos usuários locais, constatou-se que o grupo dos pescadores é o que mais conhece o ambiente, seja pela necessidade da navegação (formação rochosa) e da pesca (locais de maior oferta, maior número de indivíduos, sendo o hidrocoral “coral-de-fogo” o mais conhecido devido à fauna associada). A junção do conhecimento científico correlacionado com o contexto biogeográfico e saber local adquirido resultaram na aplicação de três práticas ambientais (desvendando as criaturas marinhas, trilha ecológica e rota subaquática) envolvendo a comunidade local conforme premissas da ciência cidadã. O contexto biogeográfico marinho atribuído às práticas para o microcosmo recifal do Seixas foi fundamentado pelos processos históricos e ecológicos de como surgiu este ambiente geológico e de onde vieram as comunidades biológicas, demonstrando as conectividades numa visão local até global dos dias atuais. Palavras-chave: ambiente recifal, geologia sedimentar, comunidade recifal, saber local, práticas ambientais.
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The "Manual de Peixes Marinhos do Sudeste do Brasil" includes all the species that occur in the area, with a brief description, geographical distribution and illustration of each one and references to the other species along the Brazilian Coast. It is based on the examination of all the specimens in the fish collection of the Museu de Zoologia da USP, and elsewhere.
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Six species of sharpnose puffers are herein recognized from the Atlantic Ocean, three of which are described as new: Canthigaster figueiredoi, n. sp. from the east coast of South America, Canthigaster jamestyleri, n. sp. from deep reefs off the southeast coast of the United States and the Gulf of Mexico, and Canthigaster supramacula, n. sp. from the west coast of Africa. Canthigaster capistratus (Lowe 1839), described from the Madeira Islands and previously considered to be a junior synonym of C. rostrata (Bloch, 1786), is revalidated and redescribed; it's known distribution extends from the Macaronesian Region to the Mediterranean. Canthigaster rostrata (Bloch, 1786), restricted to shallow-water northwestern Atlantic reefs, and C. sanctaehelenae (Günther, 1870), endemic to the mid-Atlantic islands of Ascension and St. Helena, also are diagnosed and redescribed. An identification key based on pigment pattern features is provided for all six Atlantic species of Canthigaster.
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The East Indian region (Indonesia, New Guinea, and the Philippines), with perhaps as many as 2800 species of shore fishes, has the richest marine fish fauna of the world. The numbers of species of fishes decline, in general, with distance to the east of the East Indies, ending with 566 species in Hawaii and 126 at Easier Island. The richness of the marine fauna of the East Indies is explained in terms of its relatively stable sea temperature during ice ages, its large size and high diversity of habitat, in having many families of shore fishes adapted to the nutrient-rich waters of continental and large island shelves that are lacking around oceanic islands, in having many species with larvae unable to survive in plankton-poor oceanic seas or having too short a life span in the pelagic realm for long transport in ocean currents, and in being the recipient of immigrating larvae of species that evolved peripherally. It is also a place where speciation may have occurred because of a barrier to east-west dispersal of marine fishes resulting from sea-level lowering during glacial periods (of which there have been at least 3 and perhaps as many as 6 during the last 700 000 years), combined with low salinity in the area from river discharge and cooling from upwelling. There could also have been speciation in embayments or small seas isolated in the East Indian region from sea-level lowering. Sixty-five examples are given of possible geminate pairs of fishes from such a barrier, judging from their similarity in color and morphology. Undoubtedly many more remain to be elucidated, some so similar that they remain undetected today. Fifteen examples are listed of possible geminate species of the western Indian Ocean and western Pacific that are not known to overlap in the East Indies, and 8 examples of color variants in the 2 oceans that are not currently regarded as different enough to be treated as species. Five examples of species pairs are cited for the Andaman Sea and western Indonesia that may be the result of near-isolation of the Andaman Sea during the Neogene. Explanation is given for distributions of fishes occurring only to the east and west of the East Indies in terms of extinction there during sea-level lows. The causes of antitropical distributions are discussed. The level of endemism of fishes for islands in the Pacific has been diminishing as a result of endemics being found extralimitally, as well as the discovery of new records of Indo-Pacific fishes for the areas. Hawaii still has the highest, with 23.1% endemism, and Easter Island is a close second with 22.2%. The use of subspecies is encouraged for geographically isolated populations that exhibit consistent differences but at a level notably less than that of similar sympatric species of the genus. In order to ensure continuing stability in our classification of fishes, a plea is given not to rank characters obtained from molecular and biochemical analyses higher than the basic morphological characters that are fundamental to systematics.
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The larval stage of most coral reef fishes is spent in the pelagic environment, away from the reef proper. Survival at this stage is tenuous, being mediated by factors such as food availability, predator abundance, and physical conditions. The complex biological and physical interactions of these factors can result in a seemingly stochastic larval supply that drives temporal and spatial variation in recruitment intensity. Although fish larvae are often considered strict constituents of the zooplankton community, evidence suggests that many species exhibit some form of active behavior during their pelagic stage. Variability in larval transport is determined by the interaction of water masses and the effects of external forces such as winds and tides. Active behavior by larvae may modulate some of this variability, yet a strong change in the direction or intensity of flow of a particular water mass may result in a substantial change in larval supply to a given reef or island, or may carry larvae away from a suitable food environment. The scale over which larval transport or retention occurs varies substantially among species and even among locations within a single species. For some species, larval dispersal is minimal and possibly nonexistent, whereas at the other extreme dispersal can occur over thousands of kilometers. For most coral reef fish species, with larval durations of weeks to months, transport will usually be on the scale of tens to hundreds of kilometers.