Open-access First molecular analysis of the genus Bryopsis (Bryopsidales, Chlorophyta) from Brazil, with an emphasis on the Pernambuco coast

ABSTRACT

The green algal genus Bryopsis has simple morphology and high phenotypic plasticity, making it difficult to identify its species based on morphological characteristics alone. This study evaluated the diversity of Bryopsis in northeastern Brazil (the State of Pernambuco), based on morphological and molecular data using the markers tufA and rbcL. Molecular analyses were incongruent with morphology, demonstrating the existence of cryptic and polymorphic species in the genus. Of the four taxa cited for the area based only on morphological data (Bryopsis corymbosa, B. pennata, B. plumosa, Bryopsis sp.), only B. pennata was recorded. Typical specimens of B. pennata and B. plumosa were grouped with low genetic divergence, 0-0.21 % for tufA and no divergence for rbcL, indicating that B. pennata is an extremely plastic species that includes specimens with morphotype B.plumosa”. Bryopsis pennata var. secunda is cited for the first time for northeastern Brazil, with divergence from the typical variety of 0.96-1.57 % for tufA and 0.4 % for rbcL. This study showed that broader sampling of Bryopsis is necessary in order to confirm the taxonomic status of the species referenced for Brazil, whose phenotypic plasticity may cause overestimation of diversity or reveal cryptic species.

Keywords: Bryopsis; cpDNA; macroalgae; rbcL; taxonomy; tufA

Introduction

The marine macroalgal genus Bryopsis (Bryopsidales, Chlorophyta) is one of the most diverse genera of green macroalgae with 138 species names and 84 infraspecific names, of which only 58 species names, eight varieties and five forms are currently accepted taxonomically (Guiry & Guiry 2020). Its representatives constitute a group with a predominantly marine habit, which develops mainly in areas of rocky shores and coral reefs, with temperatures ranging from five to 27 ºC (Horta et al. 2001), but they also grow in mangroves and estuaries at low salinities (Guiry & Guiry 2020). With a morphology considered simple, species of Bryopsis are characterized by non-calcified coenocytic filaments, with erect uniaxial axes with feather-like branches, called fronds, and prostate axes with a variable extension (Wynne 2005; Cremen et al. 2019). Bryopsis species have ecological importance as primary producers in aquatic ecosystems, as well as providing shelter and protection for small invertebrates (Silva 2018). The genus encompasses potentially invasive species that dominate the environment in eutrophic conditions; thus, they are considered excellent bioindicators (Williams & Smith 2007) and can cause green tides (Song et al. 2019). Due to the importance of their bioactive compounds, some species, such as Bryopsis pennata and B. plumosa have pharmacological importance, with antifungal, antibacterial and anticoagulant activities (Ibrahim et al. 2017). In addition, its compounds have been used as raw material in studies for treatments of lung and prostate cancer, tumors and acquired immunodeficiency syndrome (AIDS) (Zhang et al. 2010; Holdt & Kraan 2011; Lefranc et al. 2019) and, in the development of repellents against the mosquito Aedes aegypti (Linnaeus 1762) and A. albopictus (Skuse 1894), both recognized as vectors of arboviruses such as dengue, chikungunya, zika and yellow fever (Yu et al. 2015).

Bryopsis has a global distribution spanning polar to tropical and temperate regions (Guiry & Guiry 2020). For the tropical and subtropical western Atlantic eight species and eight varieties are currently recognized by Wynne (2017). The genus has a wide distribution on the Brazilian coast, extending from Pará state (northern Brazil) to Rio Grande do Sul state (southern Brazil) (INCT 2020), occurring also in the Oceanic Islands of Brazil: Atol das Rocas, Fernando de Noronha, São Pedro and São Paulo, Abrolhos, Trindade and Martim Vaz (Villaça et al. 2006). Five infrageneric taxa occur in Brazil, Bryopsis corymbosa, B. hypnoides, B. pennata, B. pennata var. secunda, and B. plumosa (INCT 2020). Five other taxa were reported for the Brazilian coast, Bryopsis harveyana for Bahia (Howe 1928), B. indica for São Paulo (Gepp & Gepp 1908; Joly 1957), B. rosea, with inaccurate data on collection locations (Martius 1833), Bryopsis rosea var. leprieurii for Rio de Janeiro (Zeller 1876), and Bryopsis plumosa var. leprieurii for Rio de Janeiro (Luetzelburg 1922-23) and Ceará (Schmidt 1924). However, these five citations were considered as erroneous records by Oliveira-Filho (1977), being assigned to B. plumosa (= Bryopsis plumosa var. leprieurii) or B. pennata (the other taxa). Of the five taxa correctly assigned to Brazil, three are cited for the coast of Pernambuco, B. corymbosa, B. pennata and B. plumosa (Accioly 1989; Széchy et al. 1989; Cutrim 1990; Pedrini et al. 1992; Angeiras 1995; Muñoz et al. 1997; Pereira & Accioly 1998; Pereira et al. 1996; Sousa & Cocentino 2004; Santos et al. 2006; Ribeiro et al. 2008; Simões et al. 2009; Burgos et al. 2009; Soares & Fujii 2012; Barros 2013; Carvalho et al. 2013; Silva 2013; Guimaraens et al. 2015), besides Bryopsis sp. reported by Ribeiro et al. (2008), Barros (2013) and Carvalho et al. (2013).

Many previous works on Bryopsis were focused on vegetative and reproductive morphological characters, and cytogenetic analyses (e.g., Rietema 1975; Wynne 2005). However, due to the large number of species and infraspecific categories, and the difficulty of delimiting them owing to high phenotypic plasticity and overlapping of morphological characters among its representatives, the taxonomy of the genus Bryopsis has been problematic and conflicting. Consequently, the species delimitation based on morphological analysis may lead to misidentifications and misapplied names (Krellwitz et al. 2001; Wynne 2005; Morabito et al. 2010). Likewise, life-cycle and chromosomal analyses contribute to resolution at higher taxonomic levels, making them insufficient to solve taxonomic problems at the specific level (Kapraun & Shipley 1990).

Considering the ecological and economic importance of Bryopsis, and the difficulty in properly delimiting its infrageneric and infraspecific categories, besides the recognition of cryptic and polymorphic species, molecular studies using DNA barcode techniques and phylogenetic markers have been fundamental in assessing the diversity of the genus (Krellwitz et al. 2001; Lü & Wang 2011; Hollants et al. 2013; Tufiño-Velázquez & Pedroche 2019). Plastid markers have been widely used in molecular studies to delimit green algal species, including Bryopsis, mainly tufA and rbcL genes (Provan et al. 2004; Händeler et al. 2010; Hall et al. 2010; Leliaert et al. 2014; Leliaert & Lopez-Bautista 2015; Cremen et al. 2019). TufA marker (elongation factor Tu gene) obtained the best results in the universality of the primers and quality of the sequences, being proposed as a DNA barcode for green algae, and as a phylogenetic marker as well (Saunders & Kucera 2010). Its effectiveness and successfully as DNA barcode for green algae, showing good phylogenetic resolution at generic and specific level having proven by Dijoux et al. (2012), Famà et al. (2002), Ximenes et al. (2017; 2019), followed by the rbcL (Rubisco large subunit gene) also considered suitable for phylogenetic reconstruction (Freshwater et al. 1994), having been demonstrated a sufficient level of variation to be informative in intergeneric, inter- and intraspecific studies for green and red algae as well (Freshwater & Rueness 1994; Freshwater et al. 1994; Oliveira-Carvalho et al. 2012; Leliaert et al. 2014; Ximenes et al. 2017; 2019). Both have been widely used for other genera in the Bryopsidales, such as Caulerpa, Codium, and Halimeda (Lam & Zechman 2006; Oliveira-Carvalho et al. 2012; Kazi et al. 2013; Belton et al. 2014; Ximenes et al. 2017; 2019), and also for other green algae (Mccourt et al. 2000; Shimada et al. 2003).

In this context, considering the morphological plasticity, the presence of cryptic species and the lack of molecular studies for the genus Bryopsis in Brazil, this work aimed to contribute to the understanding of the diversity of Bryopsis through the application of molecular analyses of the markers tufA and rbcL combined with the morphological traits of the species.

Materials and methods

Sampling and morphological analysis

Specimens of Bryopsis were collected along the coast of Pernambuco state (PE) (northeastern Brazil, 7º15’45’; 9º28’18” S and 34º48’35”; 41º19’54” W) at 13 sampling sites (Fig. 1), in the intertidal zone during low tide from 2016 to 2017. The area is located in the Western Atlantic Ocean in the Tropical Zone and present warm, transparent and oligotrophic waters (Horta et al. 2001). For morphological/molecular studies, each group of fronds was treated as an individual. Samples were stored in absolute ethanol and silica gel for morphological and/or molecular analyses. Part of group of fronds from a same individual was separated for molecular analyses; the remaining material was used for morphological study and pressed as herbarium vouchers.

Figure 1
Map showing the sampling sites of Bryopsis along the Pernambuco coast (northeastern Brazil).

Morphological characters were analyzed using both stereoscopic microscope Leica S6D (Wetzlar, Germany) and an optical microscope Zeiss Axioskop (Oberkochen, Germany). Photographic documentation of whole specimens and details of the different portions of the thallus and branchlets were made using a stereomicroscope Zeiss Discovery-V8 A1 (Göttingen, Germany) coupled to a digital camera Axiocam 105 Color (Göttingen, Germany), with images analyzed by the software Zeiss ZEN® (Jena, Germany); and an optical microscope Zeiss Axio Scope.A1 (Göttingen, Germany) coupled to a digital camera AxioCam MRc (Göttingen, Germany) using the software Zeiss ZEN®.

Minimum and maximum measurements were taken for morphometric characters from a set of 10 measurements for each analyzed feature in all specimens from different sampling sites. The specimens were deposited at the herbarium Prof. Vasconcelos Sobrinho of the Universidade Federal Rural de Pernambuco (PEUFR). Additional specimens from the PEUFR were also examined.

Molecular analysis

Total DNA was extracted using CTAB (cetyl trimethyl ammonium bromide) protocol as described by Oliveira-Carvalho et al. (2012). For polymerase chain reaction (PCR), the tufA marker was amplified using the primer pair tufAF (5’ TTGTTC KAACATAAA ATT GWGGTC 3’) and tufA_alg_up (5’ ATGATWACNGGHGCNGCWCAAATG 3’) (Händeler et al. 2010), following the cycle described by Händeler et al. (2010). For the marker rbcL was used the primer pair: F623-603 (5’ TCWCAACCHTYTATGCGTTGG 3’) (Curtis et al. 2008) and R1396-1372 (5’ AATTTCTTTCCAAACTTCACAAGC 3’) (Lam & Zechman 2006), following the cycle described by Curtis et al. (2008). PCR was performed using illustra PuReTaq Ready-To-Go PCR Beads kit (GE Healthcare, Buckinghamshire, UK) following the manufacturer's instructions. The fragments were amplified in a Techne TC-4000 thermocycler (Bibby Scientific Ltd, Staffordshire, UK). All PCR products were analyzed by electrophoresis in 1 % agarose to check product size and were purified using the GFXTM PCR DNA and Gel Band Purification kit (GE Healthcare, Buckinganshire, UK), following the manufacturer's instructions. Purified amplicons for both markers were sequenced using the BigDyeTM Terminator Cycle Sequencing Ready Reaction kit (Applied Biosystems, Foster City, USA), with the same primers of PCR on an ABI PRISM 3730 Genetic Analyzer (Applied Biosystems). Sequences were checked using the BlastN algorithm, through the NCBI online platform (Altschul et al. 1997). Consensus sequences and multiple alignments for both tufA and rbcL sequences were constructed using the computer program BioEdit v7.0.4.1 software (Hall 1999). For each marker, a matrix was created with the sequences generated in this study plus those available in the GenBank database used in the analyses (Tab. S1 in supplementary material).

Molecular analyzes were performed using the Neighbor-Joining (NJ) distance method in PAUP 4.0b10 program (Swofford 2002) with 2000 boostrap replicates. For phylogenetic analysis, the most appropriated model of sequence evolution for maximum likelihood (ML) and Bayesian inference (BI) was selected using jModeltest v2.1.10 (Darriba et al. 2012) under the Akaike Information Criterion (AIC) implemented on the online server CIPRES Science Gateway v3.3 (Miller et al. 2011). The model selected for tufA and rbcL was the general time-reversible model of nucleotide substitution with invariant sites and gamma distributed rates for the variable sites (GTR + I + G). The maximum likelihood analysis (ML) was performed using IQ-Tree v1.4.3 (Nguyen et al. 2015) with 1000 boostrap replicates on the IQ-Tree web portal. Bayesian Inference (BI) was performed using MrBayes v.3.2.2 program (Ronquist et al. 2012). For BI analysis, two runs with four chains of the Markov chain Monte Carlo (one hot and three cold) were used, sampling one tree every 1,000 generations for 4,000,000 generations, starting with a random tree. We discarded the first 50,000 generations in both runs as the burn-in to build the consensus tree. After discarding the trees associated with “burn-in”, a consensus tree was built for both tufA and rbcL markers. In all analyses, gaps were considered as missing data. For both tufA and rbcL matrices, the percentages of intraspecific and interspecific divergences were calculated using uncorrected ‘p’ distances in PAUP.

Results

Molecular analysis

Thirty-one new Bryopsis sequences were obtained from specimens collected on the Pernambuco coast, 19 sequences for tufA and 12 sequences for rbcL. For the tufA marker, 53 sequences were used with an alignment of 733 bp, and of the 34 sequences obtained from GenBank, three were used as outgroups, Codium tomentosum Stackhouse (KX855797), Pseudoderbesia arbuscula E.Calderon & R.Schnetter (MH591099) and Derbesia sp. (KU361860) (Tab. S2 in supplementary material).

The tufA analyses recover Bryopsis as monophyletic, with high support for NJ and moderate for ML (Fig. 2). The Brazilian sequences formed two subclades with high ML bootstrap support and high Bayesian posterior probability (PP). The major subclade grouped most of the Brazilian samples, identified as B. "plumosa" and B. pennata, with high support of ML and PP, and in which three other unidentified Bryopsis sequences (Bryopsis sp. from Oahu, USA, and Bryopsis sp.1, collected from a marine aquarium) were grouped. Except for the sample B. "plumosa" (102), all sequences of this subclade were 100 % identical, including Bryopsis sp. and Bryopsis sp.1 from GenBank. The divergence between the sample 102 and others of this subclade ranged from 0.15 % (102 vs. B. sp. and B. sp. 1) to 0.21 % (102 vs. 129). The low divergence of this subclade (0-0.21 %) indicates that all samples belong to the same genetic species. The second subclade was formed by two Brazilian samples of B. pennata var. secunda grouped with an unidentified sample of Bryopsis, named as B. sp. 28 from the Philippines, all 100 % identical, and with high to moderate support. The lack of genetic divergence between the sequences of this subclade supports the conclusion that they all correspond to the same genetic species. These two subclades, B. "plumosa"- B. pennata - B. sp.1 - B. sp. and B. pennata var. secunda - B. sp.28, differed from each other from 0.96 % to 1.57 %. For unidentified samples downloaded from GenBank that were grouped in these two subclades (B sp., B. sp.1 and B. sp.28), there are no descriptions (Leliaert et al. 2014; Wade & Sherwood 2017) that allow morphological comparison with the Brazilian material.

Figure 2
Consensus tree derived from Bayesian Inference of tufA sequences for Bryopsis taxa. NJ/ML/PP values are indicated on the branches. Only values above 60 were considered. Samples generated in this study are in bold; the number following these sequences referred to field id; - indicates lack of bootstrap support or values under 60; *indicates full support. The scale bar represents the genetic distances in substitutions per nucleotide.

Four tufA sequences of Bryopsis plumosa from GenBank were included in the analyses, and this species was shown to be paraphyletic (Fig. 2). The sample of B. plumosa from Argentina (JQ755423) was not grouped with the others from France (LN810504, FJ432653) and with another whose sampling site was not specified (U09424). These latter three sequences were split into two subclades (Fig. 2). The sequence of France (LN810504, Traon Erch, Brittany) corresponds to the complete sequencing of the chloroplast genome done by Leliaert & Lopez-Bautista (2015), and its sampling site corresponds to a region near to the type locality (Exmouth, Devon, England). The sequence LN810504 formed a subclade with Bryopsis sp. from the USA (HQ610244), being 100 % identical, and with a more divergent sequence of B. corymbosa from France (1.6 %). The other Bryopsis plumosa sequence from France (FJ432653, Pas de Calais, Boulogne-sur-Mer), generated by Verbruggen et al. (2009), is also near the type locality; however, it formed another subclade with B. plumosa (U09424), whose divergence between them was 0.99 %. The two sequences of B. plumosa from France showed high divergence (3.3 %), indicating that that belong to separate genetic species. The sample of B. plumosa from Argentina (JQ755423) proved to be highly divergent from the other sequences of B. plumosa, varying from 7.0 % to 7.2 % (Tab. 1).

Table 1
Genetic divergence values (%) of Bryopsis pennata from the Pernambuco coast and samples of B. plumosa from GenBank for the tufA marker. * Samples of B. pennata, *1 B. plumosa.

The samples identified as B. “plumosa” collected at different sites along the Pernambuco coast grouping with Bryopsis pennata samples (see above) were highly divergent from both B. plumosa from France, varying from 12.2 % to 13.6 % from LN810504, and from 12 % to 13.8 % from FJ432653, although morphologically typical plants of this species have been observed.

The eight samples identified as Bryopsis pennata positioned in this same clade, also with wide distribution on the Pernambuco coast, could not be compared molecularly with any other B. pennata tufA sequence because there are no sequences of this marker available in the databases. With the possibility of citing B. plumosa among our samples being discarded by molecular data, we maintained the identification of these samples as B. pennata, also supported by morphological analysis, with typical plants observed in different samples. Our results showed that B. pennata is extremely polymorphic, whereas the genetic divergence between samples was very low. Samples of B. pennata var. secunda also diverged in high percentage values from the B. plumosa from France (12.5-12.8 %, Tab. 2). The interspecific divergence observed between Brazilian samples and those from GenBank considered in this study ranged from 3.3-16.2 % for tufA.

Table 2
Genetic divergence values (%) of Bryopsis pennata var. secunda from the Pernambuco coast and samples of B. plumosa from GenBank for the tufA marker. *Samples of B. pennata var. secunda, *1 B. plumosa, and *2 related samples.

For rbcL, 66 sequences were used with an alignment of 1284 bp. Of the 54 sequences obtained from GenBank, Pseudoderbesia sp. (LK022434) was used as an outgroup (Fig. 3). The genetic divergences presented for rbcL were calculated on the final alignment of 1284 bp, from which the consensus tree was generated (Fig. 3). A second rbcL alignment was constructed with a larger number of Bryopsis sequences available on GenBank in order to ascertain the phylogenetic position of Brazilian samples using a larger sampling. These alignments consisted of a total of 147 sequences and, due to many sequences being partial for this marker, a shorter alignment with 689 bp was generated, from which an ML analysis was made (Fig. S1 in supplementary material). The results obtained in the two analyses were similar, with the Brazilian samples showing the same phylogenetic position (Fig. 3, Fig. S1 in supplementary material).

Figure 3
Consensus tree derived from Bayesian Inference of rbcL sequences for Bryopsis taxa. NJ/ML/PP values are indicated on the branches. Only values above 60 were considered. Samples generated in this study are in bold; the number following these sequences referred to field id; - indicates lack of bootstrap support or values under 60; *indicates full support. The scale bar represents the genetic distances in substitutions per nucleotide.

The rbcL consensus tree (Fig. 3) showed that the monophyly of Bryopsis was not supported by this gene. However, Brazilian sequences were grouped similarly to the results obtained with tufA, with high support for all analyses. The samples identified as B. pennata and B. "plumosa" are 100 % identical. The two Brazilian sequences of B. pennata var. secunda (100 % identical) were grouped into a subclade with two GenBank sequences, namely Bryopsis sp. 28, one from Tanzania (HF583394) and another from Kenya (HF583393), with high support for ML and PP. Brazilian samples of Bryopsis pennata-B. "plumosa" diverged from the var. secunda by 0.4 %. The divergence within the subclade formed by B. pennata var. secunda and Bryopsis sp. 28 was very low, ranging from 0 % (between B. pennata var. secunda and B. sp. 28 from Tanzania) to 0.15 % (between B. pennata var. secunda and B. sp. 28 from Kenya), indicating that they are the same genetic species. The genetic divergence between samples of B. pennata-B. "plumosa" and B. pennata var. secunda-B. sp. 28) for rbcL ranged from 0.27-0.4 %, being lower than that observed with tufA (Tab. 3).

Table 3
Genetic divergence values (%) of Bryopsis pennata from the Pernambuco coast and samples of B. plumosa from GenBank for the rbcL marker. *Samples of B. pennata; *1 B. pennata var. secunda; and *2 Bryopsis plumosa.

Eight rbcL sequences of Bryopsis plumosa from GenBank were included in the analyses (Fig. 3). These sequences formed four distinct clades, indicating that B. plumosa is not monophyletic, corroborating the results of tufA. Among the eight sequences analyzed, one is from Traon Erch, Brittany, France (LN810504), a region near to the type locality (Exmouth, Devon, England). The genetic divergence between replace by this sample from France and the Brazilian ones (B. "plumosa"-B. pennata) was high, 8.0 %, whereas the divergence with the samples of B. pennata var. secunda was slightly higher, 8.6 %. Another sequence of B. plumosa from France near the type locality (Pas de Calais, Boulogne-sur-Mer, FJ432637, Verbruggen et al. 2009) was positioned in a distinct clade, and diverged from B. "plumosa"-B. pennata by 6.7-6.9 % and from B. pennata var. secunda by 7.1-7.2 %. The genetic divergences observed between the Brazilian material and the B. plumosa samples from GenBank from different regions (France, Australia, Argentina and Japan) are shown in Table 3.

An rbcL sequence of Bryopsis pennata, with 562 bp (DQ469323) is available in GenBank. This sample was collected in the Virgin Islands (St. Thomas) corresponding, therefore, to a sequence of the type locality (Caribbean Sea). However, the partially amplified region of this sequence was not coincident with our sequences, not allowing a comparison between them. The intraspecific divergence observed for different taxa included in the analysis with rbcL was low. There was no genetic divergence between the four sequences of B. corymbosa from Spain and France (Fig. 3); clades formed by eight B. myosurioides sequences from South Africa, and four B. vestita sequences from New Zealand showed both 0-0.2 % of divergence; the clade with four B. cf. hypnoides 2 sequences from USA and Netherlands ranged from 0.08-0.2 %, while the four sequences that formed the B. corticulans clade from USA and Canada showed slightly higher intraspecific divergence, 0-0.3 %. However, the range of intraspecific variation for these taxa, collected in different geographical areas (0-0.3 %), remained below, although close to the limit of the divergence observed between the Brazilian sequences of B. pennata and B. pennata var. secunda, whose genetic divergence was 0.4%. Despite the lower divergence observed between these two taxa for rbcL (0.4 %) compared to tufA (0.96-1.57 %), the clades formed by B. pennata and B. pennata var. secunda were the same for both markers. The interspecific divergence observed between Brazilian samples and those from GenBank considered in this study ranged from 6.7-11.6 % for rbcL (Tab. 3).

Morphological analysis

Based on molecular analyses, two Bryopsis taxa were identified for the Pernambuco coast: B. pennata and B. pennata var. secunda. Twenty-one samples were examined; 19 were identified as B. pennata (including the morphotype B. "plumosa") and two as B. pennata var. secunda. A comparison of the morphological characters for these taxa is shown in Table 4.

Table 4
Comparison of morphological characters of Bryopsis J.V.Lamouroux from the Pernambuco coast (northeastern Brazil). D = dense, ND = not dense, PC = present continuous; PD = present discontinuous; A= absence.

Bryopsis pennata J.V.Lamouroux var. pennata Nouv. Bull. Sci. Soc. Phil. Paris. 1: 333 (Lamouroux 1809).

(Figs. 4A-O, 5A-O).

Figure 4
Bryopsis pennata. A. Habit of the thallus. B-F. Detail of fronds with regular distribution of branchlets. G-I. Detail of the variation of the apices of the thallus. J. Detail of a frond with discontinuous branchlets. K-L. Detail of fronds with irregular branchlets. (M) Detail of a frond with unilateral branchlets. N-O. Detail of the distribution of the branchlets. Note branchlets constricted at the base. Bars: A = 1 cm, B-F, J-M = 1,000 µm, G-I, N-O = 200 µm.

Figure 5
Bryopsis pennata (morphotype Bryopsisplumosa”). A. Habit of the thallus. B. Detail of the basal portion showing rhizoids. C-D. Detail of the variation of the apices of the thallus. E-M. Detail of the variation of the distribution of the branchlets on the thallus. N-O. Detail of the distribution of the branchlets. Note branchlets constricted at the base. Bars: A = 1 cm, B-D, N, O = 200 µm, E-M = 1,000 µm.

Homotypic synonym: Bryopsis plumosa var. pennata (J.V.Lamouroux) Børgesen

Heterotypic synonym: Bryopsis densa Pilger.

Type locality: Antilles, West Indies (Caribbean Sea).

For list of material examined and additional material examined see List S1 in supplementary material.

Description: Erect plants, forming small dense tufts, up to 8.0 cm high (Fig. 4A). Filamentous, coenocytic, cylindrical, flaccid in texture, dark green to light green in color, attached to the substrate by rhizoids. Frond with a linear to lanceolate outline (Fig. 4C-D). Erect filaments usually with an order of lateral branches (branchlets) of approximately uniform length along the axis, gradually smaller towards the apex of the thallus (Fig. 4E-I). Filaments generally naked in the lower portion of the thallus and with opposite branchlets, distichous or slightly alternate in the upper third, in some cases with discontinuous branching (Fig. 4J), or with branchlets arranged unilaterally (Fig. 4M). Cylindrical branchlets, without septa, constricted at the base and with obtuse apex, measuring 402-510 µm in length in the basal portions, 400-480 µm in the middle, and 20-44 µm in the apical portions. Fertile specimens not observed.

Habitat: Species very common on the Pernambuco coast. Specimens were collected in the intertidal zone, the two morphotypes (B. pennata and B. “plumosa”) often found in mixed

populations, growing on consolidated substrate (sandstone reefs). Some specimens were collected growing on Halimeda opuntia (Linnaeus) J.V.Lamouroux, Bryothamnion triquetrum(S.G.Gmelin) M.Howe, Gelidiella acerosa (Forsskål) Feldmann & Hamel, Palisada perforata (Bory) K.W.Nam, Padina gymnospora(Kützing) Sonder, Dictyota sp. and Sargussum polyceratium Montagne.

References for Pernambuco: Accioly (1989), Széchy et al. (1989), Cutrim (1990), Pedrini et al. (1992), Angeiras (1995), Pereira et al. (1996), Muñoz et al. (1997), Pereira & Accioly (1998), Sousa & Cocentino (2004), Santos et al. (2006), Ribeiro et al. (2008), Burgos et al. (2009), Soares & Fujii (2012), Barros (2013), Carvalho et al. (2013), Silva (2013), Guimaraens et al. (2015). As B. plumosa: Accioly (1989), Széchy et al. (1989), Cutrim (1990), Angeiras (1995), Simões et al. (2009), Burgos et al. (2009), Barros (2013), Carvalho et al. (2013), Silva (2013), Guimaraens et al. (2015), Soares & Fujii (2012).

Remarks: Plants of Bryopsis pennata showed great phenotypic plasticity. Samples previously identified as B. plumosa (Fig. 5A-O) based on morphological data were grouped in the same clade as B. pennata by the two markers used (tufA and rbcL), with low intraspecific divergence. Plants with morphotype B.plumosa” (Fig. 5A-O) are densely tufted, up to 12 cm high (Fig. 5A), with more dense branching in the apical portions (Fig. 5C-D), or even scarce of very unequal size. Characteristically, the fronds have a pyramidal outline, caused by the decrease in the length of the branchlets towards the apex (Fig. 5F-G). Erect filaments with one or more orders of branches distichously pinnate to bipinnate, or with slightly alternating, irregular or discontinuous branching. Branchlets are often longer in morphotype B.plumosa”, measuring 462-1040 µm in length in the basal portions, 574-1240 µm in the middle, and 354-480 µm in the apical portions (Tab. 4).

Bryopsis pennata var. secunda (Harvey) Collins & Hervey, Proc. Am. Acad. Arts Sci: 62. 1917.

(Fig. 6A-J)

Figure 6
Bryopsis pennata var. secunda. A-B. Habit of the thalli. C. Part of a tuft showing distribution of the branchlets. Note axis with unilateral branchlets. D. Detail of an axis with opposite, distichous branchlets. E-F. Detail of the apical portions of the thallus with arrangement slightly alternate distichous of the branchlets. G. Detail of the branching pattern showing two rows of branchlets overlapping unilaterally. H-I. Detail of the thallus showing branchlets with mostly unilateral distribution. J. Detail of the distribution of the branchlets. Note branchlets constricted at the base. Bars: A-B = 1 cm, C-D, I-J = 1,000 µm, E-H = 200 µm.

Basionym: Bryopsis plumosa var. secundaHarvey (1858)

Heterotypic synonym: Bryopsis harveyana J.Agardh

Type locality: Key West, Florida, USA.

Description: Erect plants forming dense tufts up to 2.0 cm high (Fig. 6A-B). Filamentous, coenocytic, cylindrical, flaccid in texture, dark green in color, attached to the substrate by rhizoids. Frond formed by two rows of branchlets with unilateral arrangement, often with the apices incurved (Fig. 6H). Erect filaments with an order of lateral branches (branchlets) of approximately uniform length, gradually smaller towards the apex (Fig. 6C-F). Filaments commonly naked in the lower third of the thallus and with opposite branchlets, distichous e/or alternate in the upper third of the thallus (Fig. 6E-F). Cylindrical branchlets, without septa, constricted at the base and with obtuse apex, measuring 415-480 µm in length in the basal portions, 560-610 µm in the middle, and 312-340 µm in the apical portions. Fertile specimens not observed.

Material examined: BRAZIL. Pernambuco: Pilar, 07°45'20.04" S - 34°49'17.25" W, IV 2017, M.F.O. Carvalho (PEUFR55185); Serrambi, 08°33'37.35" S - 35°0'58.91" W, IV 2017, M.F.O. Carvalho (PEUFR55192).

Remarks: Bryopsis pennata var. secunda is easily confused with young thalli of B. pennata due to its small size; however, it presents distinctive features such as apices of the fronds incurved and two rows of branchlets overlapping unilaterally. There is no record of this taxon for the north and northeast of Brazil, only for the states of Espírito Santo, Paraná and Santa Catarina (INCT 2020). Our examples agree morphologically with the records of Silva et al. (1996); Russell (2000); Coppejans et al. (2004). This is its first citation for northeastern Brazil.

Discussion

Previous studies on the genus Bryopsis for the Pernambuco coast, as well as for the entire Brazilian coast, were based exclusively on morphological data (Pereira & Accioly 1998). The present work constitutes the first molecular study of Bryopsis for Brazil, in which the first sequences of tufA and rbcL were generated from material collected on the Pernambuco coast. Two species were previously cited for the state of Pernambuco, B. pennata and B. plumosa (e.g., Pereira & Accioly 1998; Carvalho et al. 2013; Barros 2013). Different authors have reported the difficulty in delimiting Bryopsis species due to the high phenotypic plasticity and the overlapping of morphological characters, leading them to quote their specimens without specific identification, as Bryopsis sp. (Ribeiro et al. 2008; Burgos 2009; Barros 2013; Carvalho et al. 2013). The occurrence of B. corymbosa for Pernambuco coast (Gaibu Beach, det. Y. Ugadim, SPF-Algae 9527) may be a misidentification, in that there is only a single record based on morphological data. In addition, this species may be confused with the morphotype B. “plumosa” because they share morphological characteristics such as the irregular size of the branchlets and the branches with irregular growth. However, they differ by the gradual decrease of the branchlets length towards the apex, giving a pyramidal outline to the thallus in B. plumosa, and by the gradual decrease of the branchlets length towards the apex, giving a corymbose outline in B. corymbosa (Cormaci et al. 2014), although, according to Lee et al. (1991), intermediate characteristics are common, making it difficult to distinguish these species. In the present study, none of the specimens analyzed morphologically fit the description of B. corymbosa or were grouped with sequences of this species available in the databases. The sequences of B. corymbosa included in the molecular analyses are from the western Mediterranean (France and Spain), regions near the type locality (Livorno, Italy), and they were positioned phylogenetically distant from the Brazilian samples. Thus, the occurrence of B. corymbosa was not confirmed for the Pernambuco coast.

Our molecular and morphological results allowed us to register only the occurrence of B. pennata var. pennata and B. pennata var. secunda. Samples of B. pennata analyzed in this study proved to be extremely plastic, and the strictly morphological analyses led us to previously identify some of our specimens as B. plumosa. Table 4 compares the morphological characteristics of the studied material in regard to habit, distribution and length of branchlets. Our analyses showed that there is an overlap in most of the compared characteristics; however, B. pennata specimens had an average thallus size smaller than that identified as B.plumosa”; the latter also presented, in general, branches distributed discontinuously and longer, and often naked axes in its basal region. The diagnostic characteristics that separate B. pennata from B. plumosa are the habit and the size of the branchlets along the frond. In B. pennata, the thallus is lanceolate with branchlets uniformly sized, except near the apex, whereas in B. plumosa the thallus is pyramidal with branchlets non-uniformly sized, gradually smaller towards the apex (Krellwitz et al. 2001). In a study carried out in Praia de Serrambi (Pernambuco), Accioly (1989) observed that B. pennata occurred more frequently in the subtidal zone during the rainy season and B. plumosa in the intertidal zone during the dry season. However, our results showed that specimens of B. pennata and the B.plumosa” co-occurred in some sampling sites (Cupe, Ilha de Santo Aleixo, Enseada dos Corais) at the same distribution range (intertidal) and essentially in dry season, and it was not possible to establish any distribution pattern, even in the intertidal zonation, or attribute the morphological variations observed to differences in environmental conditions. Although plants morphologically typical of B. pennata and B. plumosa could be recognized in the studied material, our molecular results for the two markers used, clearly refuted the occurrence of B. plumosa for the Pernambuco coast because B. pennata-B.plumosa” were grouped with very low genetic divergence, 0-0.21 % for tufA, and no divergence for rbcL. Our molecular analyses showed that B. plumosa is polyphyletic with a high genetic divergence (Tabs. 1, 3), corroborating the polyphyletism previously highlighted for this species by Ciancia et al. (2012). None of the Brazilian sequences previously identified as B. plumosa matched with samples of B. plumosa available in the databases, including sequences of the genetic species of B. plumosa from the French coast of the British Channel near the type locality (Devoshire, England) and whose divergence was high (12-13.6 % for tufA and 6.7-8.4 % for rbcL), leaving no doubt that B. plumosa does not occur in the studied area. Thus, due to the phylogenetic positioning, the low genetic divergence observed between the B. pennata and “B. plumosa” and the identification of specimens morphologically typical of B. pennata in the analyzed material, we chose to cite our specimens under the name of B. pennata. Future comparisons with sequences from the type locality of B. pennata are necessary to confirm this taxon for the Pernambuco coast and Brazil.

Likewise, the sample from Argentina (JQ755423) with high genetic divergence from others B. plumosa (7.0 % to 7.2 % for tufA and 2.3-2.6 % for rbcL, Tabs. 2, 3) was generated by Ciancia et al. (2012) having been described, illustrated and sequenced for tufA and rbcL genes by these authors, confirming its identification and reinforcing to be B. plumosa, a complex of cryptic species. The recognition of cryptic and polymorphic species for Bryopsis has already been reported in previous molecular studies (Krellwitz et al. 2001; Lü & Wang 2011; Hollants et al. 2013; Tufiño-Velázquez & Pedroche 2019). Similar to that observed in our study in which B. pennata was shown to be polymorphic and included the morphotype B. "plumosa", Tufiño-Velázquez & Pedroche (2019), using the plastid psbB gene, concluded that B. pennata is the only species present in the Mexican Atlantic, and that the citations under the name of B. hypnoides and B. plumosa are names misapplied or uncertain, and even considered the possibility of B. ramulosa and B. halliae as being synonymous with B. pennata.

The analyzed specimens of B. pennata var. secunda showed diagnostic characteristics of this variety, differing from the typical variety by the small size of the frond (1.5 to 2.0 cm high in B. pennata var. secunda and 2.5 to 12 cm in B. pennata var. pennata), incurved apex, and unilateral distribution of branchlets (Tab. 4, Fig. 6C-I). Although there are no sequences of B. pennata var. secunda from the type locality (Key West, Florida, USA), available in the databases for comparison, we consider that the phylogenetic position and the genetic divergence observed between B. pennata var. secunda and the typical variety, mainly for the DNA barcode marker tufA (0.96-1.57 %), support the maintenance of the taxonomic status of Brazilian samples as var. secunda, a decision also supported by the morphological data highlighted above. This is the first citation of B. pennata var. secunda for northeastern Brazil. This variety was previously cited only for the southeast (Espírito Santo state) and southern (Paraná, Santa Catarina states) regions of Brazil (INCT 2020).

There are no studies that report the intra- and interspecific divergences for the tufA and rbcL markers for Bryopsis. However, the range of intraspecific divergence value ​​for tufA observed in this study for Brazilian samples (0-1.57 %) is relatively within the range of variation found for other Bryopsidalean genera, such as Halimeda (0-1.4 %) (Ximenes et al. 2019). The interspecific divergence observed for tufA (3.3-16.2 %) is relatively within the range reported for Halimeda, 0.9-12.4 % by Ximenes et al. (2017) and 2.0-6.2 % by Ximenes et al. (2019), as well as for Codium (Bryopsidales), 1.44-14.65 %, and Ulva (Ulvales), 0.91-9.1 % reported by Saunders & Kucera (2010)

Intraspecific divergence within Bryopsis for rbcL (0-0.4 %) was lower than that observed for Halimeda (0.8-1.2 %) by Ximenes et al. (2019), whereas the range of interspecific variation for this marker (6.7-11.6 %) is within the range reported for Halimeda, 0.8-11.7 % by Ximenes et al. (2017) and 4.5-5.0 % by Ximenes et al. (2019). For the psbB marker, Tufiño-Velázquez & Pedroche (2019) proposed a genetic distance range between 5 % to 12 % for species discrimination and, therefore, considered a distance of up to 4.9 % as intraspecific, a higher value than that obtained for tufA and rbcL in this study.

Our results from the study of the Brazilian material showed that tufA was more efficient in delimiting species (and infraspecific categories) than rbcL, confirming its use as a DNA barcode for green algae. The molecular data obtained so far for Bryopsis showed that a taxonomic revision for the genus is necessary, including a wide sampling on the Brazilian coast, in order to unveil the true diversity of the genus and clarify the taxonomic entities referenced for Brazil.

Acknowledgements

This study was financed in part by the Fundação de Amparo à Ciência e Tecnologia de (FACEPE) and Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES) - Finance Code 001. MGTO thanks the Conselho Nacional de Pesquisa e Tecnologia (CNPq) for the scholarship. VC thanks CNPq for the Productivity Fellowship (302549/2017-0).

References

  • Accioly MC. 1989. Clorofíceas marinhas bentônicas da praia de Serrambi (Município de Ipojuca-Estado de Pernambuco). Monograph, Universidade Federal Rural de Pernambuco, Recife.
  • Altschul SF, Madden TL, Schäffer AA, et al 1997. Gapped BLAST and PSI-BLAST: a new generation of protein database search programs. Nucleic Acids Research 25: 3389-3402.
  • Angeiras JAP. 1995. Clorofíceas bentônicas do litoral sul do Estado de Pernambuco. MSc Thesis, Universidade Federal Rural de Pernambuco, Recife.
  • Barros NCG. 2013. Algas marinhas bentônicas como bioindicadoras da qualidade ambiental em área recifal de Tamandaré, Pernambuco, Brasil. PhD Thesis, Universidade Federal de Pernambuco, Recife.
  • Belton GS, Reine WFPH, Huisman JM, Draisma SGA, Gurgel CFD. 2014. Resolving phenotypic plasticity and species designation in the morphologically challenging Caulerpa racemosa-peltata complex (Chlorophyta, Caulerpaceae). Journal of Phycology 50: 32-54.
  • Burgos DC, Pereira SMB, Bandeira-Pedrosa ME. 2009. Levantamento florístico das Rodofíceas do Arquipélago de São Pedro e São Paulo (ASPSP) - Brasil. Acta Botanica Brasilica 23: 1110-1118.
  • Carvalho VF, Oliveira-Carvalho MF, Pedrosa ME, Pereira SMB. 2013. Benthic chlorophytes from a coastal island in the Oriental Northeast of Brazil. Brazilian Journal of Botany 36: 203-210.
  • Ciancia M, Alberghina J, Arata PX, et al 2012. Characterization of cell wall polysaccharides of the coenocytic green seaweed Bryopsis plumosa (Bryopsidaceae, Chlorophyta) from the Argentine coast. Journal of Phycology 48: 326-335.
  • Collins FS, Hervey AB. 1917. The algae of Bermuda. Proceedings of the American Academy of Arts and Sciences 53: 1-195.
  • Coppejans E, Leliaert F, Verbruggen H, et al. 2004. The marine green and brown algae of Rodrigues (Mauritius, Indian Ocean). Journal of Natural History 38: 2959-3019.
  • Cormaci M, Furnari G, Alongi G. 2014. Flora marina bentonica del Mediterraneo: Chlorophyta. Bullettin of the Gioenia Academy of Natural Sciences of Catania 47: 11-436.
  • Cremen MCM, Leliaert F, West J, et al 2019. Reassessment of the classification of Bryopsidales (Chlorophyta) based on chloroplast phylogenomic analyses. Molecular Phylogenetics and Evolution 130: 397-405.
  • Curtis N, Dawes C, Pierce S. 2008. Phylogenetic analysis of the large subunit rubisco gene supports the exclusion of Arainvillea and Cladocephalus from the Udoteaceae (Bryopsidales, Chlorophyta). Journal of Phycology 44: 761-767.
  • Cutrim MVJ. 1990. Distribuição das macroalgas na região entremarés do recife da Praia de Piedade, Município de Jaboatão dos Guararapes (Estado de Pernambuco-Brasil). MSc Thesis, Universidade Federal Rural de Pernambuco, Recife.
  • Darriba D, Taboada GL, Doallo R, Posada D. 2012. jModelTest 2: more models, new heuristics and parallel computing. Nature Methods 9: 772-772.
  • Dijoux L, Verbruggen H, Mattio L, Duong N, Payri C. 2012. Diversity of Halimeda (Bryopsidales, Chlorophyta) in New Caledonia: a combined morphological and molecular study. Journal of Phycology 48: 1465-1481.
  • Famà P, Kooistra WCHF, Zuccarello G. 2002. Molecular phylogeny of the genus Caulerpa (Caulerpales, Chlorophyta) inferred from chloroplast tufA gene. Journal of Phycology 38: 1040-1050.
  • Freshwater DW, Fredericq S, Bradley SB, Hommersand MH, Chase MW. 1994. A gene phylogeny of the red algae (Rhodophyta) based on rbcL. Proceedings of National Academy of Sciences of the United States of America 91: 7281-7285.
  • Freshwater DW, Rueness J. 1994. Phylogenetic relationships of some European Gelidium (Gelidiales, Rhodophyta) species, based on rbcL nucleotide sequence analysis. Phycologia 33: 187-194.
  • Gepp A, Gepp ES. 1908. Marine Algae (Chlorophyceae and Phaeophyceae) and Marine Phanerogams of the ‘Sealark’Expedition, collected by J. Stanley Gardiner, MA, FRS, FLS. Transactions of the Linnean Society of London. 2nd. Series. Botany 7: 163-188.
  • Guimaraens MA, Oliveira-Carvalho MF, Aquino RE. 2015. Spatiotemporal variations of Tricolia affinis (CB Adams, 1850) associated with the macroalgal community on reef stretches at Piedade beach, southern coast of Pernambuco State, Brazil. African Journal of Plant Science 9: 196-204.
  • Guiry MD, Guiry GME. 2020. AlgaeBase. World-wide electronic publication, National University of Ireland, Galway. http://www.algaebase.org 25 Jan. 2020.
    » http://www.algaebase.org
  • Hall JA, Fucíková K, Chien L, Lewis LA, Karol KG. 2010. An assessment of proposed DNA barcodes in freshwater green algae. Cryptogamie Algologie 31: 529-555.
  • Hall TA. 1999. BioEdit: a user-friendly biological sequence alignment editor and analysis program for Windows 95/98/NT. Nucleic Acids Symposium Series. Vol. 41. London, Information Retrieval Ltd., c1979-c2000. p. 95-98.
  • Händeler K, Wägele H, Wahrmund U, Rüdinger M, Knoop V. 2010. Slugs’ last meals: molecular identification of sequestered chloroplasts from different algal origins in Sacoglossa (Opisthobranchia, Gastropoda). Molecular Ecology Resources 10: 968-978.
  • Harvey WH. 1858. Nereis boreali-americana: or, contributions to a history of the marine algae Of North America. In: Harvey W H, Mria M. (eds.) Contributions to a history of the marine algae of North America. Part III. Vol. 10. Washington, Smithsonian Institution, Chlorospermeae Smithsonian Contributions to Knowledge. p. 1-140.
  • Holdt SL, Kraan S. 2011. Bioactive compounds in seaweed: functional food applications and legislation. Journal of Applied Phycology 23: 543-597.
  • Hollants J, Leliaert F, Verbruggen H, Willems A, Clerck O. 2013. Permanent residents or temporary lodgers: characterizing intracellular bacterial communities in the siphonous green alga Bryopsis Proceedings of the Royal Society B: Biological Sciences 280: 20122659. doi: 10.1098/rspb.2012.2659
    » https://doi.org/10.1098/rspb.2012.2659
  • Horta PA, Amancio E, Coimbra CS, Oliveira EC. 2001. Considerações sobre a distribuição e origem da flora de macroalgas marinhas brasileiras. Hoehnea 28: 243-265.
  • Howe MA. 1928. Notes on some marine algae from Brazil and Barbados. Journal of the Washington Academy of Sciences 18: 186-194.
  • Ibrahim M, Salman M, Kamal S, Rehman S, Razzaq A, Akash SH. 2017. Algae-based biologically active compounds. In: Zia KM, Zuber M, Ali M. (eds.) Algae Based Polymers, Blends, and Composites. Amsterdam, Netherlands, Elsevier‎. p. 155-271.
  • INCT - Herbário Virtual da Flora e dos Fungos. 2020. http://inct.splink.org.br 13 Jan. 2020.
    » http://inct.splink.org.br
  • Joly AB. 1957. Contribuição ao conhecimento da flora ficológica marinha da Baía de Santos e Arredores. Boletim da Faculdade de Filosofia, Ciências e Letras da Universidade de São Paulo 14: 3-199.
  • Kapraun DF, Shipley MJ. 1990. Karyology and nuclear DNA quantification in Bryopsis (Chlorophyta) from North Carolina, USA. Phycologia 29: 443-453.
  • Kazi MA, Reddy CRK, Jha B. 2013. Molecular phylogeny and barcoding of Caulerpa (Bryopsidales) based on the tufA, rbcL, 18S rDNA and ITS rDNA genes. PLOS ONE 8: e82438. doi: 10.1371/journal.pone.0082438
    » https://doi.org/10.1371/journal.pone.0082438
  • Krellwitz EC, Kowallik KV, Manos PS. 2001. Molecular and morphological analyses of Bryopsis (Bryopsidales, Chlorophyta) from the western North Atlantic and Caribbean. Phycologia 40: 330-339.
  • Lam DW, Zechman FW. 2006. Phylogenetic analyses of the Bryopsidales (Ulvophyceae, Chlorophyta) based on Rubisco large subunit gene sequences. Journal of Phycology 42: 669-678.
  • Lamouroux JVF. 1809. Observations sur la physiologie des algues marines, et description de cinq nouveau genres de cette famille. Nouveau Bulletin des Sciences, par la Société Philomathique de Paris 1 : 330-333.
  • Lee WJ, Boo SM, Lee K. 1991. Notes on the genus Bryopsis (Bryopsidaceae, Chlorophyta) from Ullungdo Island, Korea. Korean Journal of Phycology 6: 23-29.
  • Lefranc F, Koutsaviti A, Ioannou E et al 2019. Algae metabolites: from in vitro growth inhibitory effects to promising anticancer activity. Natural Product Reports 36: 810-841.
  • Leliaert F, Lopez-Bautista JM. 2015. The chloroplast genomes of Bryopsis plumosa and Tydemania expeditionis (Bryopsidales, Chlorophyta): compact genomes and genes of bacterial origin. BioMed Central Genomics 16: 204. doi: 10.1186/s12864-015-1418-3
    » https://doi.org/10.1186/s12864-015-1418-3
  • Leliaert F, Verbruggen H, Vanormelingen P, et al 2014. DNA - based species delimitation in algae. European Journal of Phycology 49: 179-196.
  • Lü F, Wang G. 2011. Sequence and phylogenetic analyses of the chloroplast 16S rRNA, tufA, and rbcL genes from Bryopsis hypnoides Chinese Journal of Oceanology and Limnology 29: 922.
  • Luetzelburg P. 1922-23. Estudo Botânico do Nordeste. Vol. 1. Ministério de Viação e Obras Públicas. Rio de Janeiro, Inspetoria Federal de Obras contra as Secas.
  • Martius CFP. 1833. Algae, lichenes, hepaticae. In: Martius CFP, Eschweiler F, Nees AB, Esenbeck CG. (eds.) Flora brasiliensis seu enumeratio plantarum in Brasília tam sua sponte quam accendente cultura provenientium Vol. I. Stuttgart & Tuebingen Sumptibus J. G Cottae. p. 1-390.
  • McCourt RM, Karol KG, Bell J, et al 2000. Phylogeny of the conjugating green algae (Zygnemophyceae) based on rbcL sequences. Journal of Phycology 36: 747-758l.
  • Miller KA, Aguilar-Rosas LE, Pedroche FF. 2011. A review of non-native seaweeds from California, USA and Baja California, Mexico. Hidrobiológica 21: 365-379.
  • Morabito M, Gargiulo G, Genovese G. 2010. A review of life history pathways in Bryopsis Atti della Accademia Peloritana dei Pericolanti-Classe di Scienze Fisiche, Matematiche e Naturali. 88: C1A1002005. doi: 10.1478/C1471A1002005.
    » https://doi.org/10.1478/C1471A1002005
  • Muñoz AOM, Pereira SMB. 1997. Caracterização quali-quantitativa das comunidades de macroalgas nas formações recifais da Praia do Cupe-Pernambuco (Brasil). Trabalhos Oceanográficos da Universidade Federal de Pernambuco 25: 93-109.
  • Nguyen LT, Schmidt HA, Haeseler AV, Minh B. 2015. Q. IQ-TREE: a fast and effective stochastic algorithm for estimating maximum-likelihood phylogenies. Molecular Biology and Evolution 32: 268-274.
  • Oliveira-Carvalho MDF, Oliveira MC, Pereira SMB, Verbruggen H. 2012. Phylogenetic analysis of Codium species from Brazil, with the description of the new species C. pernambucensis (Bryopsidales, Chlorophyta). European Journal of Phycology 47: 355-365.
  • Oliveira-Filho EC. 1977. Algas marinhas bentônicas do Brasil. PhD thesis, Universidade de São Paulo, São Paulo.
  • Pedrini A, Ugadim Y, Pereira SMB, Braga MR. 1992. Algas marinhas bentônicas do Arquipélago de Fernando Noronha, Brasil. Boletim de Botânica da Universidade de São Paulo 13: 93-101.
  • Pereira SMB, Accioly MC. 1998. Clorofíceas Marinhas Bentônicas da Praia de Serrambi, Pernambuco, Brasil. Acta Botanica Brasilica 12: 25-52.
  • Pereira SMB, Mansilla AOM, Cocentino ALM. 1996. Ecological aspects of a benthic marine algal community in Southeast Bay, Archipelago of Fernando de Noronha-Brazil. Trabalhos Oceanográficos da Universidade Federal de Pernambuco 24: 157-163.
  • Provan J, Murphy S, Maggs CA. 2004. Universal plastid primers for Chlorophyta and Rhodophyta. European Journal of Phycology 39: 43-50.
  • Ribeiro FA, Travassos A, Gestinari LM, et al 2008. Análise quali-quantitativa das populações algáceas de um trecho recifal na Praia de Boa Viagem, PE. Oecologia Brasiliensis 12: 222-228.
  • Rietema H. 1975. Comparative investigations on the life-histories and reproduction of some species in the siphoneous green algal genera Bryopsis an Derbesia PhD Thesis, University of Groningen, Netherlands.
  • Ronquist F, Teslenko M, Mark PVD, et al 2012. MrBayes 3.2: efficient Bayesian phylogenetic inference and model choice across a large model space. Systematic Biology 61: 539-542.
  • Russell DJ. 2000. Identification manual for dietary vegetation of the Hawaiian green turtle Chelonia mydas Florida, USA, US Department of Commerce, National Oceanic and Atmospheric Administration, National Marine Fisheries Service, Southwest Fisheries Science Center.
  • Santos AA, Cocentino ALM, Vasconcelos-Reis TN. 2006. Macroalgas como indicadoras da qualidade ambiental da Praia de Boa Viagem-Pernambuco, Brasil. Boletim Técnico-Científico do Centro de Pesquisa e Extensão Pesqueira do Nordeste 14: 25-33.
  • Saunders GW, Kucera H. 2010. An evaluation of rbcL, tufA, UPA, LSU and ITS as DNA barcode markers for the marine green macroalgae. Cryptogamie Algologie 31: 487-528.
  • Schmidt OC. 1924. Meeresalgen der Sammlung von Lützelburg aus Brasilien. Hedwigia 65: 85-100.
  • Shimada S, Hiraoka M, Nabata S, Iima M, Masuda M. 2003. Molecular phylogenetic analyses of the Japanese Ulva and Enteromorpha (Ulvales, Ulvophyceae), with special reference to the free‐floating Ulva Phycological Research 51: 99-108.
  • Silva EG. 2013. Estrutura e composição das comunidades de Amphipodas associadas às macroalgas dos recifes de arenito da Baía de Suape, PE-Brasil. MSc Thesis, Universidade Federal de Pernambuco, Recife.
  • Silva PC, Basson PW, Moe RL. 1996. Catalogue of the benthic marine algae of the Indian Ocean. Vol. 79. California, University of California Publications in Botany.
  • Silva RSVP. 2018. Carcinofauna associada ao fital Caulerpa racemosa (Forsskål) J. Agardh e Bryopsis spp. do Arquipélago de São Pedro e São Paulo - Brasil. Tropical Oceanography 46: 1-25.
  • Simões IP, Guimaraens MA, Carvalho MFO, Valdevino J, Pereira SMB. 2009. Avaliação florística e sucessão ecológica das macroalgas em recifes na Praia de Piedade (PE). Neotropical Biology and Conservation 4: 49-56.
  • Soares LP, Fujii MT. 2012. Novas ocorrências de macroalgas marinhas bentônicas no estado de Pernambuco, Brasil. Rodriguésia 63: 557-570.
  • Song W, Wang Z, Li Y, Han H, Zhang X. 2019. Tracking the original source of the green tides in the Bohai Sea, China. Estuarine, Coastal and Shelf Science 219: 354-362.
  • Sousa GS, Cocentino ALM. 2004. Macroalgas como indicadoras da qualidade ambiental da Praia de Piedade-PE. Tropical Oceanography 32: 1-22.
  • Swofford DL. 2002. PAUP*. Phylogenetic analysis using parsimony (and other methods), version, 4, b10. Sunderland, MA, USA, Sinauer Associates.
  • Széchy MTM, Nassar CAG, Falcão C, Maurat MCS. 1989. Contribuição ao inventário das algas marinhas bentônicas de Fernando de Noronha. Rodriguésia 41: 53-61.
  • Tufiño-Velázquez RC, Pedroche FF. 2019. Las especies del género Bryopsis (Chlorophyta) presentes en las costas del Atlántico mexicano. Revista Mexicana de Biodiversidad 90: e902679. doi: 10.22201/ib.20078706e.2019.90.2679
    » https://doi.org/10.22201/ib.20078706e.2019.90.2679
  • Verbruggen H, Ashworth M, LoDuca ST, et al 2009. A multi-locus time-calibrated phylogeny of the siphonous green algae. Molecular Phylogenetics and Evolution 50: 642-653.
  • Villaça R, Pedrini AG, Pereira SMB, Figueiredo MDO. 2006. Flora marinha bentônica das ilhas oceânicas brasileiras. In: Alves RJV, Castro JWA. (eds.) Ilhas Oceânicas Brasileiras da Pesquisa ao Manejo. Brasília, Ministério do Meio Ambiente. p. 105-146.
  • Wade RM, Sherwood AR. 2017. Molecular determination of kleptoplast origins from the sea slug Plakobranchus ocellatus (Sacoglossa, Gastropoda) reveals cryptic bryopsidalean (Chlorophyta) diversity in the Hawaiian Islands. Journal of Phycology 53: 467-475.
  • Williams SL, Smith JE. 2007. A global review of the distribution, taxonomy, and impacts of introduced seaweeds. Annual Review of Ecology, Evolution, and Systematics 38: 327-359.
  • Wynne MJ. 2005. Two new species of Bryopsis (Ulvophyceae, Chlorophyta) from the Sultanate of Oman, with a census of currently recognized species in the genus. Contributions from the University of Michigan Herbarium 24: 229-256.
  • Wynne MJ. 2017. A checklist of benthic marine algae of the tropical and subtropical western Atlantic: fourth revision. Nova Hedwigia, Beihefte 145: 1-202. ISBN 978-3-443-51067-1
  • Ximenes CF, Cassano V, Oliveira-Carvalho MDF, et al 2017. Systematics of the genus Halimeda (Bryopsidales, Chlorophyta) in Brazil including the description of Halimeda jolyana sp. nov. Phycologia 56: 369-381.
  • Ximenes CF, Oliveira-Carvalho MDF, Bandeira-Pedrosa ME, Cassano V. 2019. Updates on Section Pseudo-opuntia of Halimeda: phylogenetic analyses of H. soniae sp. nov. (Bryopsidales, Chlorophyta) along the Brazilian coast. Botanica Marina 62: 327-336.
  • Yu KX, Wong CL, Ahmad R, Jantan I. 2015. Mosquitocidal and oviposition repellent activities of the extracts of seaweed Bryopsis pennata on Aedes aegypti and Aedes albopictus Molecules 20: 14082-14102.
  • Zeller G. 1876. Algae brasiliensis circa Rio de Janeiro a Dr. Glaziou, Horti publici directore collectae. In: Warming E. (ed.) Symbolae ad floram Brasiliae centralis cognoscendam. Vol. 22. Københaven, Videnskabernes Meddelelser Natur Foren. p. 426-432.
  • Zhang Z, Wang F, Wang X, Liu X., Hou Y, Zhang Q. 2010. Extraction of the polysaccharides from five algae and their potential antioxidant activity in vitro Carbohydrate Polymers 82: 118-121.

Publication Dates

  • Publication in this collection
    25 Jan 2021
  • Date of issue
    Apr-Jun 2021

History

  • Received
    13 Mar 2020
  • Accepted
    29 June 2020
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Sociedade Botânica do Brasil SCLN 307 - Bloco B - Sala 218 - Ed. Constrol Center Asa Norte CEP: 70746-520 Brasília/DF. - Alta Floresta - MT - Brazil
E-mail: acta@botanica.org.br
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