Hostname: page-component-586b7cd67f-rcrh6 Total loading time: 0 Render date: 2024-11-27T14:32:03.895Z Has data issue: false hasContentIssue false

Pelagic Sargassum and some associated mobile fauna: new records for the archipelago of Madeira (subtropical eastern Atlantic)

Published online by Cambridge University Press:  27 November 2024

S. J. Ferreira*
Affiliation:
Museu de História Natural do Funchal, Rua da Mouraria, n◦ 31, Funchal, Madeira, Portugal and MARE Madeira – Marine and Environmental Sciences Centre Madeira, Portugal
M. Kaufmann
Affiliation:
Marine Biology Station of Funchal, Faculty of Life Sciences, University of Madeira, MARE – Marine and Environmental Sciences Centre, ARNET – Aquatic Research Network, Regional Agency for the Development of Research, Technology and Innovation (ARDITI), Funchal, Portugal
P. Wirtz
Affiliation:
Centro de Ciências do Mar (CCMAR), Universidade do Algarve, 8005-139 Faro, Portugal
L. Berimbau
Affiliation:
Faculty of Sciences and Technology, University of Algarve, Campus de Gambelas, 8005-139 Faro, Portugal
R. Araújo
Affiliation:
Museu de História Natural do Funchal, Rua da Mouraria, n◦ 31, Funchal, Madeira, Portugal and MARE Madeira – Marine and Environmental Sciences Centre Madeira, Portugal
*
Corresponding author: S. J. Ferreira; Email: [email protected]
Rights & Permissions [Opens in a new window]

Abstract

Starting in the summer 2023 and peaking in late 2023, large amounts of Sargassum were observed floating off the coast of Madeira Islands, Portugal. The analysis of the samples revealed the presence of the three most common morphotypes of the two known species of pelagic Sargassum: S. natans I, S. natans VIII, and S. fluitans III. This is the first record for the subtropical eastern Atlantic Ocean for S. natans VIII and S. fluitans III. Both species were found entangled, and even though the main purpose of the study was to document the occurrence of pelagic Sargassum in the Madeira archipelago, some associated fauna were also recorded: the crab Planes minutus (Linnaeus, 1758), the amphi-Atlantic shrimps Latreutes fucorum (Fabricius, 1798) and Hippolyte coerulescens (Fabricius, 1775), and the nudibranch Scyllaea pelagica Linnaeus, 1758. The last two are new records for the Madeira archipelago.

Type
Marine Record
Copyright
Copyright © The Author(s), 2024. Published by Cambridge University Press on behalf of Marine Biological Association of the United Kingdom

Introdution

Sargassum is a brown seaweed genus that is widespread in temperate, subtropical, and tropical waters of the Atlantic, Pacific, and Indian Oceans. In the Atlantic, there are more than 60 benthic species of Sargassum and two common free-floating pelagic species, Sargassum natans (Linnaeus) Gaillon 1828 and Sargassum fluitans (Børgesen) Børgesen 1914 (Guiry and Guiry, Reference Guiry and Guiry2024).

Sargassum species are highly differentiated into holdfast, cylindrical main axis, leaflike blades and gas-filled bladders (vesicles) or pneumatocysts (Graham et al., Reference Graham, James, Wilcox and Cook2022). The two free-floating (holopelagic) species, S. natans and S. fluitans, do not have a holdfast nor are attached to a substrate at any stage of their life cycle (Parr, Reference Parr1939). As no receptacles have been observed, these two species are self-sustaining by fragmentation and vegetative reproduction (Collins and Hervey, Reference Collins and Hervey1917). Both species have distinct morphotypes, with three of them dominating the holopelagic Sargassum biomass (S. natans I, S. natans VIII, and S. fluitans III) and displaying different degrees of branching and foliation (Parr, Reference Parr1939; Schell et al., Reference Schell, Goodwin and Siuda2015; Godínez-Ortega et al., Reference Godínez-Ortega, Cuatlán-Cortés, López-Bautista and van Tussenbroek2021). There is a significant difference in growth rates among the holopelagic Sargassum morphotypes, with S. fluitans III on average doubling its biomass in 13 days, S. natans I in 22 days, and S. natans VIII in 31 days, under favourable conditions (Corbin and Oxenford, Reference Corbin and Oxenford2023). Recently, Siuda et al. (Reference Siuda, Blanfuné, Dibner, Verlaque, Boudouresque, Connan, Goodwin, Stiger-Pouvreau, Viard and Rousseau2024) proposed a revision of the names of the three most common holopelagic Sargassum morphotypes, due to their distinct morphological characteristics and sympatry within drifting aggregations: Sargassum fluitans var. fluitans (for S. fluitans III), Sargassum natans var. natans (for S. natans I), and S. natans var. wingei (for S. natans VIII).

Holopelagic Sargassum gathers in extensive rafts that serve as nursery, spawning, foraging, roosting, and protective habitat for a diversity of marine organisms, including invertebrates, sea turtles, marine birds, marine mammals, and for approximately 120 species of fish, including commercially important fisheries species (Dooley, Reference Dooley1972; Wells and Rooker, Reference Wells and Rooker2004; Doyle and Franks, Reference Doyle and Franks2015; Pries et al., Reference Pries, Netburn, Batchelor and Hermanson2023). It is a unique and ecologically significant floating marine ecosystem, providing the necessary mechanism for motile epifauna and rafting animals dispersal to new locations (Haney, Reference Haney1986; Martin et al., Reference Martin, Taylor, Huston, Goodwin, Schell and Siuda2021; Graham et al., Reference Graham, James, Wilcox and Cook2022; Pérez-Pech et al., Reference Pérez-Pech, Jesús-Navarrete and Vargas-Espositos2024). Attached to Sargassum stipes, branches, and blades there is a diversity of sessile filter-feeding fauna, which are predated by fish and invertebrate motile fauna, such as crabs, shrimps, and nudibranchs (Martin et al., Reference Martin, Taylor, Huston, Goodwin, Schell and Siuda2021). Ten invertebrates and two vertebrates are endemic to holopelagic Sargassum, with specialized coloration and morphology to camouflage within the habitat (Coston-Clements et al., Reference Coston-Clements, Settle, Hoss and Cross1991).

For centuries, explorers and oceanographers have attempted to map the holopelagic Sargassum distribution in the Atlantic Ocean. They realized that there is a general pattern, called the North Atlantic subtropical gyre, a clockwise flow of the main ocean currents (the Gulf Stream to the west, the North Atlantic Current to the north, the Canary Current to the east, and the North Equatorial Current to the south), which has the Sargasso Sea at its core (Laffoley et al., Reference Laffoley, Roe, Angel, Ardron, Bates, Boyd, Brooke, Buck, Carlson, Causey, Conte, Christiansen, Cleary, Donnelly, Earle, Edwards, Gjerde, Giovannoni, Gulick, Gollock, Hallett, Halpin, Hanel, Hemphill, Johnson, Knap, Lomas, McKenna, Miller, Miller, Ming, Moffitt, Nelson, Parson, Peters, Pitt, Rouja, Roberts, Roberts, Seigel, Siuda, Steinberg, Stevenson, Sumaila, Swartz, Thorrold, Trott and Vats2011; Lomas et al., Reference Lomas, Bates, Buck and Knap2011). In 2011, a significant mass of Sargassum was discovered in the tropical Atlantic Ocean, south of the Sargasso Sea, and it has been increasing ever since, reaching mythic proportions and forming a new consolidated region known as the ‘Great Atlantic Sargassum Belt’, that extends from the Caribbean Sea and the Gulf of Mexico to tropical West Africa (Gower et al., Reference Gower, Young and King2013; Wang et al., Reference Wang, Hu, Barnes, Mitchum, Lapointe and Montoya2019; Léger-Pigout et al., Reference Léger-Pigout, Navarro, Ménard, Ruitton, Le Loc'h, Guasco, Munaron, Thibault, Changeux, Connan, Stiger-Pouvreau, Thibaut and Michotey2024). Since then, unusually large quantities of pelagic Sargassum began to wash ashore during the spring and summer months, affecting the Caribbean islands, the coasts of Florida, Mexico, Brazil and Central America and the Atlantic coastline of tropical West Africa (Smetacek and Zingone, Reference Smetacek and Zingone2013; Bloom, Reference Bloom2015; Sissini et al., Reference Sissini, Barreto, Széchy, Lucena, Oliveira, Gower, Liu, Bastos, Milstein, Gusmão, Martinelli-Filho, Alves-Lima, Colepicolo, Ameka, Graft-Johnson, Gouvea, Torrano-Silva, Nauer, Nunes, Barufi, Rorig, Riosmena-Rodríguez, Mello, Lotufo and Horta2017; Ody et al., Reference Ody, Thibaut, Berline, Changeux, André, Chevalier, Blanfuné, Blanchot, Ruitton, Stiger-Pouvreau, Grelet, Aurelle, Guéné, Bataille, Bachelier, Guillemain, Schmidt, Fauvelle, Guasco and Ménard2019; Chávez et al., Reference Chávez, Uribe-Martínez, Cuevas, Rodríguez-Martínez, van Tusenbroek, Francisco, Estévez, Celis, Monroy-Velásquez, Leal-Bautista, Álvarez-Filip, García-Sánchez, Masia and Silva2020; Yokoyama, Reference Yokoyama2022). Now holopelagic Sargassum is found well beyond the historic boundaries of the Sargasso Sea and places these regions at the heart of local and international concerns, because of the health, economic, and environmental risks it represents (Smetacek and Zingone, Reference Smetacek and Zingone2013; Chávez et al., Reference Chávez, Uribe-Martínez, Cuevas, Rodríguez-Martínez, van Tusenbroek, Francisco, Estévez, Celis, Monroy-Velásquez, Leal-Bautista, Álvarez-Filip, García-Sánchez, Masia and Silva2020; Schuhmann et al., Reference Schuhmann, Irvine, Oxenford, Degia and Valderrama2022; Hamel et al., Reference Hamel, Garcia-Guijano, Jin and Dalton2024).

There are 11 species of Sargassum recorded for the archipelago of Madeira, 10 of them benthic and one pelagic, Sargassum natans (Buch, Reference Buch1825; Grunow, Reference Grunow and Fenzl1870; Piccone, Reference Piccone1884; Bianchi et al., Reference Bianchi, Morri, Sartoni and Wirtz1998; Parente et al., Reference Parente, Gil-Rodríguez, Haroun, Neto, de Smedt, Hernández-González and Berecibar Zugasti2000; Cruz-Reyes et al., Reference Cruz-Reyes, Gil-Rodríguez, Haroun, Parente and Hernández-González2001; Neto et al., Reference Neto, Cravo and Haroun2001; Ferreira, Reference Ferreira2011; Ferreira et al., Reference Ferreira, Gonçalves Silva and Araújo2018). The main objective of this study is to document the co-occurrence of the two species of pelagic Sargassum in the Madeira archipelago. Following the survey, four species of invertebrates frequently found in this floating ecosystem were also identified.

Material and methods

Study area

The Madeira archipelago (32.00°–33.00°N; 17.50°–16.00°W) is located in the subtropical Northeast Atlantic. It is of volcanic origin and is formed by the islands of Madeira (737 km2), Porto Santo (42 km2), Desertas (13 km2) and Selvagens (~3 km2), which are 700 km off the North African coast and almost 1000 km south of mainland Portugal (Haroun et al., Reference Haroun, Cruz-Reyes, Herrera-López, Parente and Gil- Rodríguez2002; Mata et al., Reference Mata, Fonseca, Prada, Rodrigues, Martins, Ramalho, Madeira, Cachão, Silva, Matias, Dias, Araújo, Terrinha and Kullberg2013).

The Azores subtropical anticyclone mainly determines the weather conditions in this region, which is responsible for the predominance of northeast trade winds with an average speed of 20 km h−1 (Campuzano et al., Reference Campuzano, Nunes, Malhadas, Nunes, Jardim and Neves2009). The surface ocean currents in the Madeira Archipelago are part of the general circulation of the North Atlantic current system. The eastern part of this circulation system is formed by the Azores Current, the Portugal Current, the Canary Current and the North Equatorial Current (Figure 1).

Figure 1. Geographical location of the Madeira archipelago, with the Madeira Island's sampling site location (a – Porto Moniz, b – Porto da Cruz, c – Funchal, d – Reis Magos, e – Machico) and the eastern boundary currents of the North Atlantic Subtropical Gyre (AzC, Azores Current; CaC, Canary Current; PoC, Portugal Current; NEC, North Equatorial Current; GS, Gulf Stream, NAC, North Atlantic Current).

Field work

Pelagic Sargassum and some associated mobile epifauna were collected at a few different moments of opportunity. It should be noted that the observation of large masses of these pelagic algae in the Madeira archipelago is an unpredictable event, and it was not possible to plan a sampling trip in advance. The algae mats approach the coast drifting with the current and, if they do not get stranded in a bay, they continue their journey until they drift away from the islands into the open sea. For this reason, the time available for sampling is very limited and it is necessary to always have the equipment ready for when the opportunity arises.

Sargassum specimens were collected from free-floating mats off Funchal, south coast of Madeira Island (32°35′42″N 16°56′33″W, 07/07/2023), from masses washed ashore in Porto da Cruz, north coast of Madeira Island (32°46′04″N 16°49′17″W, 17/12/2023) and at Porto Santo Island (33°3′4.62″N 16°20′38.41″W, 12/11/2023) (Figure 1). At the first two sites, the Sargassum samples were collected fresh by hand, placed in airtight bags and taken to the laboratory on the same day as collection. In Porto Santo, the samples were packed in airtight bags with seawater, kept cold in the refrigerator and transported to the laboratory the following day in a cold box. Following a thorough sorting/identification of the entire sample, using Parr (Reference Parr1939) and Godínez-Ortega et al. (Reference Godínez-Ortega, Cuatlán-Cortés, López-Bautista and van Tussenbroek2021), both species of pelagic Sargassum (S. natans I, S. natans VIII, and S. fluitans III) were found at these three sampling sites. Two specimens of each morphotype were selected, per sampling site, dry in herbarium sheets and incorporated into the Natural History Museum of Funchal herbarium (MADM), with also some fragments preserved in silica gel and others in 4% Formalin.

Throughout the pelagic Sargassum sampling, it was observed that there was a large amount of associated epifauna visible to the naked eye. Although collecting epifauna was not the initial aim of the study, the authors decided to take the opportunity to collect samples of the most visible and common organisms found in the pelagic Sargassum samples. They were carefully separated from the substrate, by rinsing each sample of pelagic Sargassum with fresh water into a container and collecting the specimens that were loose from the algae. They were then identified, placed in specimen jars according to their taxonomic classification (20 individuals of each species), preserved in 70% alcohol and incorporated into the collection of the Natural History Museum of Funchal (MMF) and of the Naturalis Biodiversity Center, Leiden, Netherlands (RMNH).

Floating and stranded Sargassum mats were also observed and photographed, at Porto Moniz (north coast of Madeira), Porto Santo, Desertas, and Selvagens islands (Figure 2).

Figure 2. Accumulation of pelagic Sargassum in (A) Porto Moniz harbour (northwest coast of Madeira Island), (B) Porto Santo Island, (C) Deserta Grande (Desertas islands), (D) Selvagem Pequena, and (E) Selvagem Grande. Photo credits: Henrique Rodrigues, Ricardo Araújo, Isamberto Silva, and Manuel José de Jesus.

Results

Macroalgal records

Sargassum fluitans (Børgesen) Børgesen 1914
Material examined: MADM4150, MADM4152, MADM4153, MADM4155
Sargassum natans (Linnaeus) Gaillon

Material examined: MADM4149, MADM4151, MADM4154, MADM4156

Remarks: Sargassum fluitans and Sargassum natans specimens were collected entangled, free-floating, or in large mats that washed ashore in Funchal, Porto da Cruz and Porto Santo. Unlike S. natans, S. fluitans has thorny stems, which is the main determining feature that distinguishes these two pelagic Sargassum species (Parr, Reference Parr1939).

The specimens collected belong to the three morphotypes commonly found in Sargassum masses drifting in the Atlantic Ocean, Sargassum fluitans III, Sargassum natans I and VIII. S. fluitans III has small thorns along the stems, lacks apical spines on oblong bladders and has short, narrow blades; S. natans I has smooth stems (without thorns), narrow blades and apical spines on spherical bladders; S. natans VIII has thick and smooth stems (without thorns), spherical bladders rarely adorned with apical spine and has long, broad, and widely spaced blades (Parr, Reference Parr1939; Schell et al., Reference Schell, Goodwin and Siuda2015; Martin et al., Reference Martin, Taylor, Huston, Goodwin, Schell and Siuda2021) (Figure 3).

Figure 3. Three holopelagic Sargassum morphotypes recorded in the coastal waters of Madeira archipelago.

a. Sargassum natans I, with smooth stems, narrow blades and spherical bladders with apical spines; b. Sargassum natans VIII, with thick and smooth stems, long, broad, and widely spaced blades and spherical bladders rarely adorned with apical spine; c. Sargassum fluitans III, with small thorns along the stem, short and narrow blades and oblong bladders without apical spines.

Sargassum natans was previously recorded in Madeira (Buch, Reference Buch1825) and it is very likely that this observation might have been morphotype S. natans I. According to Parr (Reference Parr1939) in early observations of S. natans the dominant morphotype in the Sargasso Sea was S. natans I, while S. natans VIII was extremely rare (and isolated to the Caribbean) until the recent proliferation of the GASB (Schell et al., Reference Schell, Goodwin and Siuda2015; García-Sánchez et al., Reference García-Sánchez, Graham, Vera, Escalante-Mancera, Álvarez-Filip and van Tussenbroek2020). To the best of our knowledge, for S. natans VIII and for S. fluitans III this is the first record for the subtropical eastern Atlantic Ocean.

Mobile Epifaunal Records (Figure 4)
Hippolyte coerulescens (Fabricius, 1775) (Figure 4A)

Material examined: MMF50302, MMF50303, MMF50304, MMF50305, MMF50306, MMF50307, MMF 50311, RMNH.CRUS.D.59355.

Figure 4. (A) Hippolyte coerulescens (Fabricius, 1775), (B) Latreutes fucorum (Fabricius, 1798), (C) Scyllaea pelagica Linnaeus, 1758, and (D) Planes minutus (Linnaeus, 1758) Photo credits: Luís Berimbau.

The specimens were found with Sargassum floating off Madeira Island. This amphi-Atlantic shrimp is usually associated with floating Sargassum (Coston-Clements et al., Reference Coston-Clements, Settle, Hoss and Cross1991). In the eastern Atlantic, H. coerulescens has previously been reported from the Azores (Lenz and Strunck, Reference Lenz and Strunck1914), the Canary Islands (Ortmann, Reference Ortmann and Hensen1893), and the Cape Verde Islands (Ortmann, Reference Ortmann and Hensen1893) but not yet from Madeira archipelago.

Latreutes fucorum (Fabricius, 1798) (Figure 4B)

Material examined: RMNH.CRUS.D.59354

This amphi-Atlantic shrimp species was also common on floating Sargassum off Madeira Island. It is known to live not only with pelagic Sargassum but also on benthic algae (Sivertsen and Holthuis, Reference Sivertsen and Holthuis1956; Chace, Reference Chace1972; Coston-Clements et al., Reference Coston-Clements, Settle, Hoss and Cross1991; Udekem D'Acoz, Reference Udenkem D'Acoz1999) and has been recorded from Madeira previously (Wirtz, Reference Wirtz2020).

Scyllaea pelagica Linnaeus, 1758 (Figure 4C)

Material examined: MMF50310, MMF50313, MMF50314

This amphi-Atlantic nudibranch species lives on floating algae (Pola et al., Reference Pola, Camacho-Garcia and Gosliner2012). It was common on Sargasssum floating off Madeira Island. In the eastern Atlantic, S. pelagica has been recorded south of Madeira, e.g. at the Canary Islands (Ortea et al., Reference Ortea, Moro, Bacallado and Caballer2014) but apparently not yet at Madeira Island or north of it.

Planes minutus (Linnaeus, 1758) (Figure 4D)

Material examined: MMF50312; RMNH.CRUS.D.59356

This amphi-Atlantic crab was by far the most common crustacean on Sargassum floating off Madeira and Porto Santo. It is known from Madeira archipelago, mainly associated with marine turtles and drifting debris (Manning and Holthuis, Reference Manning and Holthuis1981; Dellinger et al., Reference Dellinger, Davenport and Wirtz1997; Araújo and Wirtz, Reference Araújo and Wirtz2015). Planes minutus has already been reported for Madeira and the Azores by Lenz and Strunck (Reference Lenz and Strunck1914) and for the Canary Islands by Heller (Reference Heller1863).

Some other species were observed associated with the pelagic Sargassum, like Argonauta argo Linnaeus, 1758 and Schedophilus ovalis (Cuvier, 1833), which were photographed but not collected (Figure 5).

Figure 5. (A) Argonauta argo Linnaeus, 1758 and (B) Schedophilus ovalis (Cuvier, 1833). Photo credits: Luís Berimbau.

Discussion

Since 2011, scientists worldwide are investigating the cause of the sudden increase in holopelagic Sargassum in the Atlantic Ocean, which was first noticed in the Madeira archipelago in 2023. Although the causes are not yet fully understood, there are several hypotheses that could explain this extreme event: an abnormal wind regime between 2009 and 2010 in the east-central Atlantic Ocean that led to the movement of Sargassum to the far eastern North Atlantic (Johns et al., Reference Johns, Lumpkin, Putman, Smith, Muller-Karger, Rueda-Roa, Hu, Wang, Brooks, Gramer and Werner2020), an enrichment of nutrients from the Amazon, Pará, and Orinoco rivers (Djakouré et al., Reference Djakouré, Araujo, Hounsou-Gbo, Noriega and Bourlès2017; Aquino et al., Reference Aquino, Noriega, Mascarenhas, Costa, Monteiro, Santana, Silva, Prestes, Araujo and Rollnic2022), an increase in dust from the Sahara desert (Johnson et al., Reference Johnson, Ko, Franks, Moreno and Sanchez-Rubio2012), a change in upwelling patterns off the north-east coast of Africa (Wang et al., Reference Wang, Hu, Barnes, Mitchum, Lapointe and Montoya2019) and an increase in sea temperature (Johns et al., Reference Johns, Lumpkin, Putman, Smith, Muller-Karger, Rueda-Roa, Hu, Wang, Brooks, Gramer and Werner2020). Nevertheless, investigating such a large-scale phenomenon must involve the study of physical and biological processes, like the physical transport of floating Sargassum and its growth in response to changing oceanic conditions (Berline et al., Reference Berline, Ody, Jouanno, Chevalier, André, Thibaut and Ménard2020; Corbin and Oxenford, Reference Corbin and Oxenford2023).

It is a fact that since 2011 there is a concomitant increase in holopelagic Sargassum beach landing events in the Caribbean Sea, the Caribbean coasts of Central America and Mexico, and on the Atlantic coastline of tropical West Africa (Gower et al., Reference Gower, Young and King2013; Franks et al., Reference Franks, Johnson and Ko2016; Wang et al., Reference Wang, Hu, Barnes, Mitchum, Lapointe and Montoya2019). The large growth in biomass increases the chance that some of this Sargassum might enter the Gulf Stream and then drifts along the subtropical gyre to the waters of the Madeira archipelago, crossing the Atlantic Ocean. It must be emphasized that this is not an unprecedented event, whenever meteo-oceanographic conditions are favourable, small amounts of holopelagic Sargassum can occasionally be found in the area of Madeira (Menezes, Reference Menezes1926; Levring, Reference Levring1974). What is unusual is the quantity that has been recorded since the end of 2023, in which large ‘rafts’ of Sargassum have washed up on the coast of the islands of Madeira, Desertas, Porto Santo, and Selvagens. There are also reports of large masses of holopelagic Sargassum washing up on the coasts of the Azores islands, having increased in volume since January 2024, following storms from the western Atlantic Ocean (Gabriel et al., Reference Gabriel, Maridakis and Fredericq2024; J. Faria, personal communication to SJF).

Although we have not yet observed any negative impact on the coastal ecosystems of the Madeira archipelago, we do have access to the record of what has happened in the affected areas since 2011, were many environmental, health, and economic impacts have already been reported, such as the decrease in biodiversity, with the death of marine organisms as a result of the destruction of their habitats (McLawrence et al., Reference McLawrence, Sealy and Roberts2017; van Tussenbroek et al., Reference Van Tussenbroek, Arana, Rodríguez-Martínez, Espinoza-Avalos, Canizales-Flores, González-Godoy, Barba-Santos, Vega-Zepeda and Collado-Vides2017; UNEP-CEP, 2021; López-González et al., Reference López-González, Lucho-Constantino and López-Pérez2023). Therefore, the recent influx of drifting holopelagic Sargassum approaching the coast of the Madeira archipelago needs a thorough monitoring effort, and, if necessary, some of the measures adopted in the coastal areas affected by this phenomenon should be implemented.

This could be a one-off situation, with a few occasional fragments of holopelagic Sargassum from the East Atlantic reaching the Madeira archipelago, or we could be facing a new reality. Whether it will become something common in the future, possibly seasonal, reflecting the changes taking place in the ocean, we will only know in the next few years. In the meantime, we should be vigilant and take the opportunity to study this phenomenon more thoroughly, tracking the frequency and intensity of these events and assessing any potential negative impacts on local biodiversity, possibly alongside researchers on the other eastern Atlantic islands that have been ‘visited’ by these floating algae.

Data

The data that support this study are in the Natural History Museum of Funchal (MMF) and in the Naturalis Biodiversity Center, Leiden (RMNH) collections and can be made available under request.

Acknowledgements

Special thanks to Ysabel Gonçalves and Pedro Sepúlveda for collecting some specimens of Sargassum and delivering them to the Natural History Museum of Funchal. To Henrique Rodrigues, Isamberto Silva, and Manuel José de Jesus for allowing us to use photographs of their authorship. To Daniela Gabriel and João Faria for giving us feedback about the Sargassum occurrence in the Azores.

Author Contributions

Study conception and design: SJF, LB, PW; data collection: PW, MK, RA; analysis and interpretation of results: SJF, PW, MK, RA, LB; wrote first draft: SJF; revision and edits to manuscript: PW, SJF, MK, RA; final approval of submitted manuscript: all authors.

Financial Support

This research received no specific grant from any funding agency, commercial, or not-for-profit sectors.

Conflict of Interest

The authors declare none.

References

Aquino, R, Noriega, C, Mascarenhas, A, Costa, M, Monteiro, S, Santana, L, Silva, I, Prestes, Y, Araujo, M and Rollnic, M (2022) Possible Amazonian contribution to Sargassum enhancement on the Amazon Continental Shelf. Science of the Total Environment 853, 158432.CrossRefGoogle ScholarPubMed
Araújo, R and Wirtz, P (2015) The decapod crustaceans (Crustacea Decapoda) of Madeira Island – an annotated checklist. Spixiana 38/2, 205218.Google Scholar
Berline, L, Ody, A, Jouanno, J, Chevalier, C, André, J-M, Thibaut, T and Ménard, F (2020) Hinscasting the 2017 dispersal of Sargassum algae in the Tropical North Atlantic. Marine Pollution Bulletin 158, 111431.CrossRefGoogle ScholarPubMed
Bianchi, CN, Morri, C, Sartoni, G and Wirtz, P (1998) Sublittoral epibenthic communities around Funchal (ilha da Madeira, NE Atlantic). Boletim do Museu de História Natural do Funchal Sup. 5, 5980.Google Scholar
Bloom, L (2015) Caribbean Clogged: Seaweed Invasion Takes Over Beaches. Available at https://www.yahoo.com/travel/caribbean-clogged-seaweed-invasion-takes-over-125850888537.html (Accessed: 1 October 2024).Google Scholar
Buch, IV (1825) Physikalische Beschreibung der Kanarischen Inseln. Berlin: Hofdruckerei von Königlichen Akademie, 2 vols. xiV+388+381 pp.Google Scholar
Campuzano, FJ, Nunes, S, Malhadas, M, Nunes, D, Jardim, M and Neves, R (2009) Modelação da Hidrodinâmica da Orla Sul da ilha da Madeira. 6as Jornadas Portuguesas de engenharia Costeira e Portuária, Funchal (8 e 9 de outubro).Google Scholar
Chace, FA Jr (1972) The shrimps of the Smithsonian-Bredin Caribbean Expeditions with a summary of the West Indian shallow-water species (Crustacea: Decapoda: Natantia). Smithsonian Contributions to Zoology 98, 1179.Google Scholar
Chávez, V, Uribe-Martínez, A, Cuevas, E, Rodríguez-Martínez, RE, van Tusenbroek, BI, Francisco, V, Estévez, M, Celis, LB, Monroy-Velásquez, LV, Leal-Bautista, R, Álvarez-Filip, L, García-Sánchez, M, Masia, L and Silva, R (2020) Massive influx of pelagic Sargassum spp. on the coasts of the Mexican Caribbean 2014–2020: challenges and opportunities. Water 12, 2908.CrossRefGoogle Scholar
Collins, FS and Hervey, AB (1917) The algae of Bermuda. Proceedings of the American Academy of Arts and Sciences 53, 3183.CrossRefGoogle Scholar
Corbin, M and Oxenford, H (2023) Assessing growth of pelagic sargassum in the tropical Atlantic. Aquatic Botany 187, 103654.CrossRefGoogle Scholar
Coston-Clements, L, Settle, LR, Hoss, DE and Cross, FA (1991) Utilization of the Sargassum habitat by marine invertebrates and vertebrates: a review. NOAA Technical Memorandum NMFS-SEFSC-296, 32 p.Google Scholar
Cruz-Reyes, A, Gil-Rodríguez, MC, Haroun, RJ, Parente, MI and Hernández-González, CL (2001) Flora y Vegetación Bentónica de Porto Santo. Academia Canaria de Ciencias XIII, 3148.Google Scholar
Dellinger, T, Davenport, J and Wirtz, P (1997) Comparisons of social structure of Columbus crabs living on loggerhead sea turtles and inanimate flotsam. Journal of the Marine Biological Association of the United Kingdom 77, 185194.CrossRefGoogle Scholar
Djakouré, S, Araujo, M, Hounsou-Gbo, A, Noriega, C and Bourlès, B (2017) On the potential causes of the recent Pelagic Sargassum blooms events in the tropical North Atlantic Ocean, Biogeosciences Discuss. [preprint], https://doi.org/10.5194/bg-2017-346, in review.Google Scholar
Dooley, JK (1972) Fishes associated with the pelagic Sargassum complex, with a discussion of the Sargassum community. Contributions in Marine Science 16, 132.Google Scholar
Doyle, E and Franks, J (2015) Sargassum Fact Sheet. Marathon, FL: Gulf and Caribbean Fisheries Institute, 3pp. http://dx.doi.org/10.25607/OBP-784Google Scholar
Ferreira, SJ (2011) Contributo para o estudo das macroalgas do intertidal da ilha da Madeira. Diversidade, distribuição e sazonalidade (Dissertação de mestrado). Universidade da Madeira, Portugal, 112 p.Google Scholar
Ferreira, SJ, Gonçalves Silva, JJ and Araújo, R (2018) Marine algae collection in the herbarium of the Funchal Natural History Museum (MADM) with new records from the archipelago of Madeira. Boletim do Museu de História Natural do Funchal 68, 3152.Google Scholar
Franks, JS, Johnson, DR and Ko, DS (2016) Pelagic Sargassum in the tropical North Atlantic. Gulf and Caribbean Research 27, SC6SC11.CrossRefGoogle Scholar
Gabriel, D, Maridakis, C and Fredericq, S (2024) Gone with the wind: an unexpected Sargassum inundation in the mid-Atlantic Azores archipelago. Marine Pollution Bulletin 204, 116522.CrossRefGoogle ScholarPubMed
García-Sánchez, M, Graham, C, Vera, E, Escalante-Mancera, E, Álvarez-Filip, L and van Tussenbroek, BI (2020) Temporal changes in the composition and biomass of beached pelagic Sargassum species in the Mexican Caribbean. Aquatic Botany 167, 103275. doi: 10.1016/j.aquabot.2020.103275CrossRefGoogle Scholar
Godínez-Ortega, JL, Cuatlán-Cortés, JV, López-Bautista, JM and van Tussenbroek, BI (2021) A natural history of floating Sargassum species (Sargasso) from Mexico. IntechOpen, 135. doi: 10.5772/intechopen.97230Google Scholar
Gower, J, Young, E and King, S (2013) Satellite images suggest a new Sargassum source region in 2011. Remote Sensing Letters 4, 764773.CrossRefGoogle Scholar
Graham, LE, James, MG, Wilcox, LW and Cook, ME (2022) Algae, 4th Edn. LJLM Press, University of Wisconsin-Madison and Illinois State University.Google Scholar
Grunow, A (1870) Die algen. In Fenzl, E (ed.), Reise der öSterrechischen Fregatte Novara um die Erde in den Jahren 1857, 1858, 1859, Botanischer Theil. Wien: Erster Band, pp. 198.Google Scholar
Guiry, MD and Guiry, GM (2024) AlgaeBase. Galway: World-wide electronic publication, National University of Ireland. Available at https://www.algaebase.org; searched on 17 May 2024.Google Scholar
Hamel, K, Garcia-Guijano, C, Jin, D and Dalton, T (2024) Perceived Sargassum event incidente, impacts, and management response in the Caribbean Basin. Marine Policy 165, 106214.CrossRefGoogle Scholar
Haney, JC (1986) Seabird patchiness in tropical oceanic waters: the influence of Sargassum “Reefs”. The Auk 103, 141151.CrossRefGoogle Scholar
Haroun, RJ, Cruz-Reyes, A, Herrera-López, G, Parente, MI and Gil- Rodríguez, MC (2002) Flora Marina de la Isla de Madeira: Resultados de la Expedición “Macaronesia 2000”. Revista de la Academia Canaria de Ciencias 14, 3752.Google Scholar
Heller, C (1863) Die crustaceen des südlichen Europa. Crustacea Podophtalmia. Wien: Wilhelm Braumüller, pp. 1336.Google Scholar
Johns, EM, Lumpkin, R, Putman, NF, Smith, RH, Muller-Karger, FE, Rueda-Roa, DT, Hu, C, Wang, M, Brooks, MT, Gramer, LJ and Werner, FE (2020) The establishment of a pelagic Sargassum population in the tropical Atlantic: biological consequences of a basin-scale long distance dispersal event. Progress in Oceanography 182, 102269.CrossRefGoogle Scholar
Johnson, DR, Ko, DS, Franks, JS, Moreno, P and Sanchez-Rubio, G (2012) The Sargassum Invasion of the Eastern Caribbean and Dynamics of the Equatorial North Atlantic. Proceedings of the 65th Gulf and Caribbean Fisheries Institute 5–9 November 2012 Santa Marta, Colombia.Google Scholar
Laffoley, DA, Roe, HSJ, Angel, MV, Ardron, J, Bates, NR, Boyd, IL, Brooke, S, Buck, KN, Carlson, CA, Causey, B, Conte, MH, Christiansen, S, Cleary, J, Donnelly, J, Earle, SA, Edwards, R, Gjerde, KM, Giovannoni, SJ, Gulick, S, Gollock, M, Hallett, J, Halpin, P, Hanel, R, Hemphill, A, Johnson, RJ, Knap, AH, Lomas, MW, McKenna, SA, Miller, MJ, Miller, PI, Ming, FW, Moffitt, R, Nelson, NB, Parson, L, Peters, AJ, Pitt, J, Rouja, P, Roberts, J, Roberts, J, Seigel, DA, Siuda, ANS, Steinberg, DK, Stevenson, A, Sumaila, VR, Swartz, W, Thorrold, S, Trott, TM and Vats, V (2011) The protection and management of the Sargasso Sea: The golden floating rainforest of the Atlantic Ocean. Summary Science and Supporting Evidence Case. Sargasso Sea Alliance, 44 pp.Google Scholar
Léger-Pigout, M, Navarro, E, Ménard, F, Ruitton, S, Le Loc'h, F, Guasco, S, Munaron, J-M, Thibault, D, Changeux, T, Connan, S, Stiger-Pouvreau, V, Thibaut, T and Michotey, V (2024) Predominant heterotrophic diazotrophic bacteria are involved in Sargassum proliferation in the Great Atlantic Sargassum belt. The ISME Journal 18, 19.CrossRefGoogle ScholarPubMed
Lenz, H and Strunck, K (1914) Die dekapoden der deutschen südpolar-expedition 1901–1903 I. Brachyuren und macruren mit auschluss der sergestiden. – Deutsche südpolar-expedition 15. Zoologie 7, 257376, pis. 12–22.Google Scholar
Levring, T (1974) The marine algae of the archipelago of Madeira. Boletim do Museu Municipal do Funchal 28, 5111.Google Scholar
Lomas, MW, Bates, NR, Buck, KN and Knap, AH (eds) (2011) Oceanography of the Sargasso Sea: Overview of Scientific Studies. Sargasso Sea Alliance Science Report Series, 5, 64 pp. ISBN 978-0-9847520-7-2.Google Scholar
López-González, IE, Lucho-Constantino, CA and López-Pérez, PA (2023) La invasión de sagazo: de un problema ambiental a un área de oportunidad. Tópicos de Investigación en Ciencias de la Tierra y Materiales 10, 1826.CrossRefGoogle Scholar
Manning, RB and Holthuis, LB (1981) West African brachyuran crabs (Crustacea: Decapoda). Smithsonian Contributions to Zoology 306, 1379.CrossRefGoogle Scholar
Martin, LM, Taylor, M, Huston, G, Goodwin, DS, Schell, JM and Siuda, ANS (2021) Pelagic Sargassum morphotypes support different rafting motile epifauna communities. Marine Biology 168, 115.CrossRefGoogle Scholar
Mata, J, Fonseca, P, Prada, S, Rodrigues, D, Martins, S, Ramalho, R, Madeira, J, Cachão, M, Silva, C and Matias, MJ (2013) O Arquipélago da Madeira. In Dias, R, Araújo, A, Terrinha, P and Kullberg, JC (eds), Geologia de Portugal, 1st Edn. Lisboa: Escolar Editora, pp. 14851540.Google Scholar
McLawrence, JL, Sealy, H and Roberts, D (2017) The impacts and challenges of the 2015 Sargassum seaweed invasion in the Caribbean. International Journal of Ecology and Environmental Sciences 43, 309317.Google Scholar
Menezes, CA (1926) Contribuição para o estudo das algas da Madeira. Broteria, série botânica 22, 7178.Google Scholar
Neto, AI, Cravo, DC and Haroun, RT (2001) Checklist of the benthic marine plants of the Madeira archipelago. Botanica Marina 44, 391414.CrossRefGoogle Scholar
Ody, A, Thibaut, T, Berline, L, Changeux, T, André, J-M, Chevalier, C, Blanfuné, A, Blanchot, J, Ruitton, S, Stiger-Pouvreau, V, Grelet, J, Aurelle, D, Guéné, M, Bataille, H, Bachelier, C, Guillemain, D, Schmidt, N, Fauvelle, V, Guasco, S and Ménard, F (2019) From in situ to satellite observations of pelagic Sargassum distribution and aggregation in the tropical north Atlantic Ocean. PLoS ONE 14, e0222584.CrossRefGoogle ScholarPubMed
Ortea, J, Moro, L, Bacallado, JJ and Caballer, M (2014) Nuevas especies y primeras citas de babosas marinas (Mollusca: Opisthobranchia) en las islas Canarias y en otros archipiélagos de la Macaronesia. Vieraea 42, 4777.CrossRefGoogle Scholar
Ortmann, AE (1893) Decapoden und schizopoden. In Hensen, V (ed.), Ergebnisse der Plankton-Expedition der Humboldt-Stiftung, vol. 2. Kiel und Leipzig: Lipsius und Tischer, pp. 1120, 7p.Google Scholar
Parente, MI, Gil-Rodríguez, MC, Haroun, RJ, Neto, AI, de Smedt, G, Hernández-González, CL and Berecibar Zugasti, E (2000) Flora marina de las Ilhas Selvagens: resultados preliminares de la expedición “Macaronesia 2000”. Revista de la Academia Canaria de Ciencias 12, 920.Google Scholar
Parr, AE (1939) Quantitative observations on the pelagic Sargassum vegetation of the western north Atlantic with preliminary discussion of morphology and relationships. Bulletin of the Bingham Oceanographic Collection, Peabody Museum of Natural History, Yale University, VI, 7.Google Scholar
Pérez-Pech, WA, Jesús-Navarrete, A and Vargas-Espositos, AA (2024) Does sargassum contribute to meiofauna dispersal? The case of tardigrades and nematodes in the Mexican Caribbean. Marine Environmental Research 195, 106349.CrossRefGoogle ScholarPubMed
Piccone, A (1884) Crociera del Corsaro alle Isole Madera e Canarie del Capitano Enrico d'Albertis. Alghe, Genova: Tipografia del R. Istituto Sordo-Muti, pp. [3][60, 1 pl.CrossRefGoogle Scholar
Pola, M, Camacho-Garcia, YE and Gosliner, TM (2012) Molecular data illuminate cryptic nudibranch species: the evolution of the Scyllaeidae (Nudibranchia: Dendronotina) with a revision of Notobryon. Zoological Journal of the Linnean Society 165, 311336.CrossRefGoogle Scholar
Pries, A, Netburn, AN, Batchelor, H and Hermanson, VR (2023) A little bit os Sargassum goes a long way: seafloor observations of Sargassum fluitans and Sargassum natans in the Western Atlantic Ocean. Frontiers in Marine Science 10, 1250150.CrossRefGoogle Scholar
Schell, JM, Goodwin, DS and Siuda, ANS (2015) Recent Sargassum inundation events in the Caribbean: shipboard observations reveal dominance of a previously rare form. Oceanography 28, 810.CrossRefGoogle Scholar
Schuhmann, PW, Irvine, J, Oxenford, HA, Degia, AK and Valderrama, JP (2022) The potential economic impacts of sargassum inundations in the Caribbean, Part 1: Insights from the literature. SargAdapt Project Report, FINAL DRAFT. Centre for Resource Management and Environmental Studies (CERMES), University of the West Indies, Cave Hill, Barbados, 57pp.Google Scholar
Sissini, MN, Barreto, MBBB, Széchy, MTM, Lucena, MB, Oliveira, MC, Gower, J, Liu, G, Bastos, EO, Milstein, D, Gusmão, F, Martinelli-Filho, JE, Alves-Lima, C, Colepicolo, P, Ameka, G, Graft-Johnson, K, Gouvea, L, Torrano-Silva, B, Nauer, F, Nunes, JMC, Barufi, JB, Rorig, L, Riosmena-Rodríguez, R, Mello, TJ, Lotufo, LVC and Horta, PA (2017) The floating Sargassum (Phaeophyceae) of the South Atlantic Ocean – likely scenarios. Phycologia 56, 321328.CrossRefGoogle Scholar
Siuda, ANS, Blanfuné, A, Dibner, S, Verlaque, M, Boudouresque, C-F, Connan, S, Goodwin, DS, Stiger-Pouvreau, V, Viard, F and Rousseau, F (2024) Morphological and molecular characters differentiate common morphotypes of Atlantic holopelagic Sargassum. Phycology 4, 256275.CrossRefGoogle Scholar
Sivertsen, E and Holthuis, LB (1956) Crustacea Decapoda (The Penaeidea and Stenopodidea excepted). Report of the scientific results of the “Michael Sars”. North Atlantic Deep-sea Expedition 1910 5, 154.Google Scholar
Smetacek, V and Zingone, A (2013) Green and golden seaweed tides on the rise. Nature 504, 8488.CrossRefGoogle ScholarPubMed
Udenkem D'Acoz, C (1999) Inventaire et distribution des crustacés decápodes de l'Atlantique nord-oriental, de la Méditerranée et des eux continentales adjacentes au nord de 25°N. Patrimoines naturels, Muséum national d'Histoire naturelle, Paris, 40: 383 p.Google Scholar
UNEP–CEP, United Nations Environment Programme- Caribbean Environment Programme (2021) Sargassum White Paper – Turning the crisis into an opportunity. Ninth Meeting of the Scientific and Technical Advisory Committee (STAC) to the Protocol Concerning Specially Protected Areas and Wildlife (SPAW) in the Wider Caribbean Region. Kingston, Jamaica.Google Scholar
Van Tussenbroek, BI, Arana, HAH, Rodríguez-Martínez, RE, Espinoza-Avalos, J, Canizales-Flores, HM, González-Godoy, CE, Barba-Santos, MG, Vega-Zepeda, A and Collado-Vides, L (2017) Severe impacts of brown tides caused by Sargassum spp. on near-shore Carribean seagrass communities. Marine Pollution Bulletin 122, 272281.CrossRefGoogle Scholar
Wang, M, Hu, C, Barnes, BB, Mitchum, G, Lapointe, B and Montoya, JP (2019) The great Atlantic Sargassum belt. Science (New York, N.Y.) 365, 8387.CrossRefGoogle ScholarPubMed
Wells, DR and Rooker, J (2004) Spatial and temporal patterns of habitat use by fishes associated with Sargassum mats in the northwestern Gulf of Mexico. Bulletin of Marine Science 74, 8199.Google Scholar
Wirtz, P (2020) A pictorial catalogue of the shallow-water Hippolytidae, Thoridae, and Lysmatidae of Madeira Island. Available at https://www.researchgate.net/publication/344738495_A_pictorial_catalogue_of_the_shallow-water_Hippolytidae_Thoridae_and_Lysmatidae_of_Madeira_IslandGoogle Scholar
Yokoyama, M (2022) Suddenly, Sargassum! How a seaweed changed St. Martin. Edited by Jenn Yerkes. Les Fruits de Mer, pp. 52.Google Scholar
Figure 0

Figure 1. Geographical location of the Madeira archipelago, with the Madeira Island's sampling site location (a – Porto Moniz, b – Porto da Cruz, c – Funchal, d – Reis Magos, e – Machico) and the eastern boundary currents of the North Atlantic Subtropical Gyre (AzC, Azores Current; CaC, Canary Current; PoC, Portugal Current; NEC, North Equatorial Current; GS, Gulf Stream, NAC, North Atlantic Current).

Figure 1

Figure 2. Accumulation of pelagic Sargassum in (A) Porto Moniz harbour (northwest coast of Madeira Island), (B) Porto Santo Island, (C) Deserta Grande (Desertas islands), (D) Selvagem Pequena, and (E) Selvagem Grande. Photo credits: Henrique Rodrigues, Ricardo Araújo, Isamberto Silva, and Manuel José de Jesus.

Figure 2

Figure 3. Three holopelagic Sargassum morphotypes recorded in the coastal waters of Madeira archipelago.a. Sargassum natans I, with smooth stems, narrow blades and spherical bladders with apical spines; b. Sargassum natans VIII, with thick and smooth stems, long, broad, and widely spaced blades and spherical bladders rarely adorned with apical spine; c. Sargassum fluitans III, with small thorns along the stem, short and narrow blades and oblong bladders without apical spines.

Figure 3

Figure 4. (A) Hippolyte coerulescens (Fabricius, 1775), (B) Latreutes fucorum (Fabricius, 1798), (C) Scyllaea pelagica Linnaeus, 1758, and (D) Planes minutus (Linnaeus, 1758) Photo credits: Luís Berimbau.

Figure 4

Figure 5. (A) Argonauta argo Linnaeus, 1758 and (B) Schedophilus ovalis (Cuvier, 1833). Photo credits: Luís Berimbau.