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Molecular phylogeny of pelagic Sargassum
Ethan Alley1, 2, Alesia Hunter1, 3, Walter Hutcheson1, 4, Kate Petersen,1, 5, Katherine Running1, 6
SEA Semester: Marine Biodiversity and Conservation Class C266 April 18-May 19, 2016
1- Sea Education Association, Woods Hole, Massachusetts, 2- Harvard College, Cambridge, Massachusetts, 3- Beloit College, Beloit,
Wisconsin, 4- New York University, New York, New York, 5- The Evergreen State College, Olympia, Washington, 6- American University,
Washington, District of Columbia
Acknowledgements
We wish to express our sincere gratitude to Amy Siuda, Laura Cooney, and Matt Hirsch
for their invaluable research advice and lab assistance. Additionally, we extend thanks to Robbie
Smith for sample collection and moral support at sea. We are grateful to the C266 staff and crew
for their companionship, mentorship, and support of our work aboard the SSV Corwith Cramer.
We are indebted to the past SEA Semester research cruises and Sea Education Association for
their sample collection and preservation. We also would like to express our appreciation to
Annette Govindarajan for her guidance with analyzing our molecular results. Special thanks to
the Virginia Wellington Cabot Foundation for contributing funding towards the Marine
Biodiversity and Conservation program at Sea Education Association.
Abstract
Pelagic Sargassum specimens were collected and preserved at eight stations on four
separate Sea Education Association (Woods Hole, Massachusetts, USA) research cruises
undertaken between April 2015 and April 2016 in the tropical Atlantic Ocean, Caribbean, and
Sargasso Sea. Collected specimens included Sargassum natans I, S. natans VIII, S. fluitans III,
and two morphologically distinct samples, Sargassum sp. Deoxyribonucleic acid (DNA) was
extracted from the specimens and the mtsp and rbcL-S genetic marker regions were amplified
and sequenced. S. fluitans III and S. natans (I and VIII) are shown to be 1.5% genetically distant
at the concatenated sequence of these loci. Mtsp had 10 single nucleotide polymorphisms (SNPs)
(2.4%) and rbcL-S had 2 SNPs and a 9 basepair insertion (1.6%). S. fluitans III and S. natans (I
and VIII) showed consistent allelic differences at both loci. No variability was found between S.
natans I and S. natans VIII. Sargassum sp. was found to be molecularly distinguished from both
S. fluitans III and S. natans (I and VIII) at the mtsp locus. The phylogeny showed that S. natans I
and S. natans VIII are more closely related to each other than they are to S. fluitans III, with
Sargassum sp. as an intermediate taxa. Our results do not support species delineation between S.
natans I and S. natans VIII. These results support but do not confirm S. natans and S. fluitans
species delineations. The analysis of Sargassum sp. suggests the possibility of cryptic diversity
in pelagic Sargassum.
Introduction
As a foundation taxon, Sargassum provides otherwise rare deep ocean surface substrate
to complex localized communities of epibiont and motile fauna (Stoner and Greening 1984;
Casazza and Ross 2008). Over 200 marine species associate with pelagic Sargassum including
endemic species such as the Sargassum frogfish (Histrio histrio), Sargassum crab (Planes spp.),
and Slender Sargassum shrimp (Latreutes fucorum), which exhibit color matching and plant
mimicry adaptive strategies (Coston-Clements 1991; Hacker and Madin 1991; Trott et al. 2011).
These pelagic communities provide food, shelter and nursery grounds for a variety of threatened
and economically important taxa such as sea turtles (Carr and Meylan 1980; Carr 1987; Luschi et
al. 2003), tuna (Coston-Clements 1991), and dolphinfish (Oxenford and Hunte 1999).
Due to its primary and significant ecosystem functions and vulnerability to damage from
pollution (Powers et al. 2013) and commercial extraction (Laffoley et al. 2011), pelagic
Sargassum is of conservation concern (South Atlantic Fishery Management Council 2002;
United Nations Environment Programme 2012; Sargasso Sea Commission 2014). Further, a
small study suggested that the species composition of Sargassum associated communities may
have changed over the last 40 years (Huffard 2014), with unknown ramifications for pelagic
ecology. The authors pointed out that ocean temperature and acidity increased concurrently and
suggested more research to investigate this correlation. Additional research is required to verify
Sargassum associated community changes.
Øjvind Winge (1923) and Albert Parr (1939) developed the taxonomic classification
system currently used to describe pelagic Sargassum (Genus Sargassum, subgenus Sargassum,
section Sargassum), which is based on morphological characters such as the presence or absence
of stem thorns and the size and shape of bladders and leaf blades. Parr (1939) described two
species, Sargassum natans and Sargassum fluitans, which have 6 morphological forms: S. natans
I, S. natans II, S. natans VIII, S. natans IX, S. fluitans III, and S. fluitans X. These form
variations are not commonly addressed in modern field guides (Schneider and Searles 1991;
Littler and Littler 2000; Dawes and Mathieson 2008) or scientific literature (Stoner and Greening
1984; Calder 1995) which tend to only refer to S. natans or S. fluitans (most likely referring to S.
natans I and S. fluitans III). This is probably due to the seemingly ubiquitous nature of S. natans
I and S. fluitans III throughout their range (A. N. S. Siuda pers. comm.).
Distinguishing between Sargassum forms in scientific research is necessary because
Sargassum species and form identity appears to be a driver of species abundance and diversity in
Sargassum-associated pelagic ecosystems. For example, a study of S. natans and S. fluitans
found that these species support distinct hydroid species assemblages (Calder 1995). In another
study, Litiopa melanostoma, a common snail, was found to be more abundant on S. natans than
on S. fluitans (Stoner and Greening 1984). No form distinctions were made in either study.
Winge (1923) also observed prolific hydroid colonization on S. fluitans III and very limited
colonization on S. natans II. The only ecological study addressing S. natans I, S. natans VIII, and
S. fluitans III found species diversity differences between the three forms, with S. natans VIII
having the lowest diversity (L. M. Martin unpubl.).
Unprecedented and economically disruptive Sargassum beach inundation events were
reported in 2011, 2012, 2014, and 2015 in the western Caribbean and Gulf of Mexico (Higgins
2011; MercoPress 2015). Some news outlets suggested that the inundations came from the
Sargasso Sea (Boodram 2015; Miller 2015), an area of the north Atlantic Ocean named for its
Sargassum population. However satellite data and backtracking analysis suggested a previously
unknown equatorial Atlantic source (Johnson et al. 2012; Gower et al. 2013). Both S. natans and
S. fluitans (without form descriptions) were implicated in the inundations by various sources
(Johnson et al. 2012; Economist 2015; Fardin et al. 2015). However, verified morphological
identifications and voucher specimen collections were sparse and not always accurate. For
instance, Szechy et al. (2012) reported an equatorial Atlantic S. natans bloom in 2011, but
voucher photographs clearly show S. fluitans specimens, which can be conclusively identified by
the presence of thorns on the stem (Parr 1939). Further complicating the investigation of the
beach inundations was the identification of huge quantities of floating S. natans VIII in 2014
(Schell et al. 2015), a form that had not been treated in the literature since Parr (1939). Schell et
al. (2015) subsequently documented S. natans VIII throughout the tropical Atlantic Ocean,
Caribbean, Antilles Current, and southern Sargasso Sea, a phenomena not previously observed
during their 20 years of shipboard research.
The confusion surrounding the Sargassum beach inundation events underlines the need to
clarify ambiguities in species and form definitions, which complicate Sargassum research at a
time when form distribution and abundance may be changing and original baseline data is
limited. The lack of widespread treatment of the different morphological forms in the literature
challenges the development of functional ecological narratives regarding pelagic Sargassum. The
degree to which existing ecological data for pelagic Sargassum could be confounded by incorrect
or incomplete species or form identification is unknown.
As a complex and morphologically plastic taxa (Kilar 1992), molecular techniques are
necessary to corroborate and refine morphological species and form delineations in Sargassum.
Genetic markers used previously to delineate taxa in Sargassum and other brown algae groups
include the chloroplastic Ribulose bisphosphate carboxylase large chain + spacer + partial
Ribulose bisphosphate carboxylase small chain (rbcL-S) (N. E. Phillips unpubl.; Phillips et al.
2005; Dixon et al. 2014), the nuclear Internal Transcribed Spacer 2 (ITS-2) (Stiger et al. 2000,
2003; Mattio et al. 2010), and the mitochondrial cytochrome oxidase 3 subunit (cox3) (Mattio et
al. 2008, 2009; Dixon et al. 2014). In these studies, the rbcL-S, ITS-2, and cox3 markers were
successfully used to obtain consistent phylogenetic resolution at the subsections level or higher,
but resulted in shallow unresolved trees below the subsection level.
An additional marker, the mitochondrial intergenic spacer region (mstp) between the
mitochondrial 23S gene and transcription ribonucleic acid Valine (tRNA-Val), was proposed for
use within Sargassum and other Sargassaceae by Draisma et al. (2010) after development for use
in the Fucus genus by Coyer et al. (2006). This non-coding region was shown to be the most
variable of those studied, but could not be aligned for a multi-genus data set (Draisma et al.
2010). A subsequent marker assessment analysis of ITS-2, the chloroplast partial RubisCO
operon (rbcL-S), cox3, mtsp and the mitochondrial cytochrome oxidase unit 1 gene (Co1) by
Mattio and Payri (2010) identified mtsp as a potentially useful barcoding marker, but also found
difficulties in alignment.
Although analyses of these loci have produced important taxonomic insights across the
genus in benthic species, molecular phylogeny of pelagic Sargassum is highly understudied. A
2015 study of S. fluitans III, S. natans I, and S. natans VIII at the CO1 marker found a single
nucleotide difference between S. fluitans III and S. natans (I and VIII), but no variation between
S. natans I and S. natans VIII at this locus (A.N.S. Suida pers.comm.). Camacho et al. (2015)
included two samples identified as S. natans and two identified as S. fluitans in a molecular
phylogeny of Sargassum subgenus Sargassum from the Caribbean and western tropical Atlantic
using ITS-2, rbcL-S, and cox3. Form distinctions were not made in this study. As a whole, the
phylogeny constructed from these markers did not have sufficient resolution within Sargassum
sect. Sargassum. When the pelagic species’ sequences were retrieved from GenBank and
examined, only rbcL-S appeared to be variable between S. natans and S. fluitans. Camacho et al.
(2015) also sequenced mtsp but did not include these sequences in the phylogeny due to
alignment difficulty. However, mtsp was one of the few markers to show any variability within
Sargassum sect. Sargassum (O. Camacho pers.comm.).
In this study, we amplify and sequence rbcL-S and mtsp loci of pelagic Sargassum which
represent the predominant morphological forms collected in the Sargasso Sea, western tropical
Atlantic and Caribbean, S. natans I, S. natans VIII, and S. fluitans III, as well as two specimens
of Sargassum sp. (provisionally identified as S. natans II) collected in the south Sargasso Sea.
We then construct a molecular phylogeny based on these markers.
Methods
Pelagic Sargassum specimens were collected and preserved at eight stations on four
separate Sea Education Association (Woods Hole, Massachusetts, USA) research cruises (C259,
C263, C264, and C266) undertaken between April 2015 and April 2016 in the tropical Atlantic
Ocean, Caribbean, and Sargasso Sea (Table 1). Sampling from a broad geographic area was
necessary due to the minimally overlapping ranges of pelagic Sargassum forms (Schell et al.
2015). Every 12 hours along these cruise tracks, at 0000 h and 1200 h, a one-meter wide, half-
meter high Neuston net with 333-micrometer mesh was deployed. The net was towed at a speed
of two to three knots for 30 minutes, for a total approximate sampling distance of one nautical
mile. Concurrent sampling using a dip net with 333-micrometer mesh occurred at morning
stations. Sargassum was preserved in silica for molecular analysis when at least seven
individuals of a particular morphological form were collected at a single station. All specimens
were identified using morphological characters described by Parr (1939). Morphological
vouchers for all samples were collected and are kept at Sea Education Association.
A 5-10 cm sample was clipped from the apical end of each Sargassum replicate and
persistent epiphytes were removed with a razor blade. The samples were then rinsed in
freshwater and dried in silica desiccant for at least 48 hours before extraction. Two to four leaf
blades or an approximately equivalent volume of floats and stems from the dried samples were
ground in 1.5 ml microcentrifuge tubes using disposable pellet pestles.
DNA was extracted using MoBio Power Plant Pro Kit (Carlsbad, California, USA)
according to manufacturer protocols as modified by Wilson et al. (2016) to replace the bead
beating step with 24hrs of heating at 65°C with periodic vortexing. Extractions were cleaned
using MoBio Power Clean Pro Kit according to manufacturer protocols. The clean genomic
DNA was profiled using a Nanodrop ND-1000 Spectrophotometer.
A mitochondrial spacer (mtsp), and the chloroplast-encoded partial Ribulose
bisphosphate carboxylase large chain + spacer + partial Ribulose bisphosphate carboxylase small
chain (rbcL-S) regions were amplified using Polymerase Chain Reaction (PCR). PCR products
were amplified using site-specific primers (Table 2) and reaction protocols were optimized from
those developed by Coyer et al. (2006) for mtsp and Mattio et al. (2008) for rbcL-S. The cycling
conditions included: (i) a 4 minute initial denaturation at 95°C, (ii) 40 cycles of a 40 second
denaturation at 95°C, (iii) a 30 second annealing at 50°C (mtsp), 45°C (rbcL-S), (iv) a 45 second
extension at 68°C, and (v) a 7 minute final extension at 68°C. New England Biolabs HotTaq 2x
Master Mix with Standard Buffer (Ipswich, Massachusetts, USA) was used for all reactions.
PCR products were verified with agarose gel electrophoresis. PCR products were purified
with Qiagen Qiaquick PCR Cleanup Kit (Germantown, Maryland, USA). The DNA
concentration of purified PCR products was quantified with a Nanodrop ND-1000
Spectrophotometer. Purified PCR products were sequenced by Eurofins MWG Operon
(Huntsville, Alabama, USA) in both directions with primers from the amplification step (Table
2) using the Sanger sequencing method. In total, this analysis included 13 replicates of
Sargassum natans VIII, 15 replicates of Sargassum natans I, 14 replicates of Sargassum fluitans
III, and two replicates of Sargassum sp., which were morphologically distinct specimens
suggestive of Sargassum natans II.
Results
This study produced 65 sequences for mtsp and 49 for rbcL-S which are available on
Genbank (Table 3). Sequences were aligned with ClustalW (Larkin et al. 2007) in Geneious
9.1.7 software (Biomatters Ltd.) to an appropriate outgroup obtained from Genbank via the
National Center for Biotechnology Information’s Basic Local Alignment Search Tool (NCBI
BLAST). The mtsp alignment was 195 base pairs (bp) long including a two and three bp gap
introduced by the outgroup comparison. This is significantly shorter than previously reported
(Coyer et al. 2006, Draisma et al. 2010). The rbcL-S alignment was longer, at 687 bp, including
a 9 bp gap. Both alignments were examined and it was determined that all sequences from
Sargassum natans I and Sargassum natans VIII were identical to one another at both the mtsp
and rbcL-S loci. All S. fluitans III sequences were also identical to one another at each loci.
Lastly, the sequences obtained from Sargassum sp. were found to be identical to one another at
both loci.
We discovered 10 polymorphic loci (5.2%) in mtsp at which S. fluitans III and S. natans I
and VIII showed a consistent allelic pattern, which corresponded exactly to the species
delineation (S. natans or S. fluitans). We found 2 polymorphic loci and a 9 bp indel in the rbcL-S
sequences, which also corresponded to the S. natans/S. fluitans delineation and did not vary
between the morphological forms of S. natans (.2%).
Sequences from samples with both rbcL-S and mtsp represented in the alignments were
concatenated for S. natans I (n=15), S. natans VIII (n=13), S. fluitans III (n=14), and Sargassum
sp. (n=2) resulting in a combined alignment of 882 bp. Identical sequences for each form were
removed. Gaps in both sequences were treated according to the simple indel coding method of
Simmons and Ochoterena (2000) to inform the phylogeny.
A consensus Neighbor Joining Tree was constructed from the concatenated, gap-coded
sequences in Geneious 9.1.7 software (Biomatters Ltd.) using the Tamura-Nei genetic distance
model with 10,000 bootstrap replications and a support threshold of 95% (Figure 1). The
concatenated consensus tree showed genetic distance of 1.5% between S. natans (I and VIII) and
S. fluitans III, .07% between S. natans (I and VIII) and Sargassum sp., and .08% between
Sargassum sp. and S. fluitans III. Genetic distances were also calculated for each locus
individually (not concatenated) using the same parameters above. This showed rbcL-S was less
variable, with .4% genetic distance between S. natans (I and VIII) and S. fluitans III, .4% genetic
distance between Sargassum sp. and S. fluitans III, and no distance between S. natans (I and
VIII) and Sargassum sp. Contrarily, mtsp alone produced genetic distances of 5.5% between S.
natans (I and VIII) and S. fluitans III, 5.6% between S. natans (I and VIII) and Sargassum sp.,
and 2.2% between Sargassum sp. and S. fluitans III.
Discussion
We found genetic distance between S. fluitans III and S. natans (I and VIII) at both the
mtsp (5.5%) and rbcL-S (.4%) loci. This finding corroborates the morphologically based species
delineations proposed by Parr (1939) as well as the 1 SNP difference observed in Co1 between
these taxa (A.N.S. Siuda pers. comm.). Our observed variation does not meet the criteria for
species delineations proposed by Mattio and Payri (2010) who conducted the only study of the
effectiveness of various genetic markers as barcodes for Sargassum subgenus Sargassum. This
study included the section Sargassum, to which pelagic Sargassum belongs, along with a number
of additional sections, but did not include any samples from pelagic Sargassum. The authors
reported a range of interspecific genetic distances for mtsp (16-19.5%) and rbcL-S (1-6%)
(Mattio and Payri 2010), much higher than the genetic distances found between our S. natans
group and S. fluitans III at these loci.
Difficulty resolving closely related taxa at or below the section level within the
Sargassum genus is not uncommon (Phillips 2005; Mattio et al. 2010; Dixon et al. 2014). N. E.
Phillips (unpubl.) argues that there is unlikely to be a universal pattern of genetic variation for
spacer regions in macroalgae, because these regions demonstrate distinct patterns of variation
depending on the studied taxa. It may be that the barcode assessment of Mattio and Payri (2010)
was too broad to definitively represent Sargassum sect. Sargassum and that this section has
patterns of genetic variation distinct from other sections in subgenus Sargassum. This hypothesis
is corroborated by the observation that excluding Sargassum sect. Sargassum from barcode
analysis changed the identification success of all markers especially rbcL-S (Mattio and Payri
2010) and the evidence that a molecular phylogeny with the best known markers was unable to
resolve between species within Sargassum section Sargassum (Camacho et al. 2015). The
section has been noted as a primary target for barcode development efforts because “...no good
barcoding marker will be identified for the genus Sargassum before one can genetically
discriminate between the very closely related and morphologically distinct species of S. section
Sargassum” (Mattio and Payri 2010).
We found S. natans I and S. natans VIII to be genetically identical at the mtsp and rbcL-S
loci despite the fact that both morphological forms possess distinct morphological characters
(Parr 1939; Schell et al. 2015) and associated ecological communities (L.M. Martin unpubl.).
This data corroborates the previously mentioned Co1 marker study which also found no
difference between these forms (A.N.S. Siuda pers. comm.) However, our results clearly show
that S. natans I and S. natans VIII, traditionally considered to be morphological variants of the
same species, are more closely related to each other than they are to either S. fluitans III or
Sargassum sp. This highlights important areas of future research, both for development of new
genetic markers to resolve evolutionary relationships in pelagic Sargassum and to investigate
how distinct phenotypes and ecological characteristics can arise from yet undiscovered genetic
variation.
We found that Sargassum sp. was .07% distant from S. natans (I and VIII) and .08%
distant from S. fluitans III, suggesting the possibility of cryptic diversity in pelagic Sargassum.
These samples had subtle, but noticeable morphological differences which resembled S. natans II
(Parr 1939). Unfortunately, we were unable to complete our identification before the majority of
our specimens were discarded. More specimens are required to determine whether this form was
described by Parr (1939) and that the observed grouping is not anomalous. This finding
illustrates the importance of further integrative taxonomy research on the less common
morphological forms of pelagic Sargassum, which could clarify evolutionary relationships and
may also contribute to the understanding of inter and intraspecific genetic diversity in Sargassum
sect. Sargassum.
Further research is also necessary to establish new genetic markers within Sargassum
sect. Sargassum to facilitate integrative taxonomy work, with barcoding assessments on large
representative samples from within the section. Lastly, research into life history and reproduction
patterns of pelagic Sargassum could clarify morphological changes that occur during an
individual’s life cycle.
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Table 1: Station summary information for samples of each morphological form.
Date Position Region # Samples
Sargassum natans VIII
26 Nov 2015 16°20’N x 33°20’W E. Tropical Atlantic 9
7 Dec 2015 14°54’N x 53°04’W W. Tropical Atlantic 4
Sargassum fluitans III
7 Dec 2015 14°54’ N x 53°04’W W. Tropical Atlantic 4
21 Feb 2016 17°56’N x 65°06’W E. Caribbean 10
Sargassum natans I
26 Apr 2015 25°00’N x 67°09’W Sargasso Sea 7
11 May 2015 32°55’N x 65°20’W Sargasso Sea 8
Other:
Sargassum sp.
20 Apr 2016 18°40.9'N x 66°9.7'W Tropical Atlantic 1
24 Apr 2016 24°10.7'N x66°44.2'W Sargasso Sea 1
Table 2: Primers used to isolate the selected markers from genomic DNA. AT = PCR annealing
temperature (°C).
Marker Primer Primer sequence Reference AT
mtsp mtsp-F 5′ CGTTTGGCGAGAACCTTACC-3′ Coyer et al. 2006 50
mtsp-R 5′ TACCACTGAGTTATTGCTCCC-3′ Coyer et al. 2006 50
rbcL-S 3F 5′-CATCGTGCTGGTAACTCTAC-3′ Mattio et al.
2008
45
S97R 5′-CATCTGTCCATTCWACACTAAC-3′ Mattio et al.
2008
45
Table 3: GenBank accession numbers for sequenced samples
Figure 1: Consensus Neighbor Joining Tree of the concatenated rbcL-S and mtsp loci. Bootstrap
support is indicated at nodes, with those less than 95% supported collapsed. Number of replicates
of each sequence shown in parentheses. Branch length is unconstrained and corresponds to
genetic distance at a scale of 0.002. Outgroup sequences obtained from GenBank using NCBI
Blast.