TY - JOUR
T1 - Non-indigenous seaweeds in the Northeast Atlantic Ocean, the Mediterranean Sea and Macaronesia
T2 - a critical synthesis of diversity, spatial and temporal patterns
AU - van der Loos, Luna M.
AU - Bafort, Quinten
AU - Bosch, Samuel
AU - Ballesteros, Enric
AU - Bárbara, Ignacio
AU - Berecibar, Estibaliz
AU - Blanfuné, Aurélie
AU - Bogaert, Kenny
AU - Bouckenooghe, Silke
AU - Boudouresque, Charles François
AU - Brodie, Juliet
AU - Cecere, Ester
AU - Díaz-Tapia, Pilar
AU - Engelen, Aschwin H.
AU - Gunnarsson, Karl
AU - Shabaka, Soha Hamdy
AU - Hoffman, Razy
AU - Husa, Vivian
AU - Israel, Álvaro
AU - Karremans, Mart
AU - Knoop, Jessica
AU - Le Gall, Line
AU - Maggs, Christine A.
AU - Mineur, Frédéric
AU - Parente, Manuela
AU - Perk, Frank
AU - Petrocelli, Antonella
AU - Rodríguez-Prieto, Conxi
AU - Ruitton, Sandrine
AU - Sansón, Marta
AU - Serrão, Ester A.
AU - Sfriso, Adriano
AU - Sjøtun, Kjersti
AU - Stiger-Pouvreau, Valérie
AU - Surget, Gwladys
AU - Taşkin, Ergün
AU - Thibaut, Thierry
AU - Tsiamis, Konstantinos
AU - Van De Weghe, Lotte
AU - Verlaque, Marc
AU - Viard, Frédérique
AU - Vranken, Sofie
AU - Leliaert, Frederik
AU - De Clerck, Olivier
N1 - Publisher Copyright:
© 2023 British Phycological Society.
PY - 2024
Y1 - 2024
N2 - Effective monitoring of non-indigenous seaweeds and combatting their effects relies on a solid confirmation of the non-indigenous status of the respective species. We critically analysed the status of presumed non-indigenous seaweed species reported from the Mediterranean Sea, the Northeast Atlantic Ocean and Macaronesia, resulting in a list of 140 species whose non-indigenous nature is undisputed. For an additional 87 species it is unclear if they are native or non-indigenous (cryptogenic species) or their identity requires confirmation (data deficient species). We discuss the factors underlying both taxonomic and biogeographic uncertainties and outline recommendations to reduce uncertainty about the non-indigenous status of seaweeds. Our dataset consisted of over 19,000 distribution records, half of which can be attributed to only five species (Sargassum muticum, Bonnemaisonia hamifera, Asparagopsis armata, Caulerpa cylindracea and Colpomenia peregrina), while 56 species (40%) are recorded no more than once or twice. In addition, our analyses revealed considerable variation in the diversity of non-indigenous species between the geographic regions. The Eastern Mediterranean Sea is home to the largest fraction of non-indigenous seaweed species, the majority of which have a Red Sea or Indo-Pacific origin and have entered the Mediterranean Sea mostly via the Suez Canal. Non-indigenous seaweeds with native ranges situated in the Northwest Pacific make up a large fraction of the total in the Western Mediterranean Sea, Lusitania and Northern Europe, followed by non-indigenous species with a presumed Australasian origin. Uncertainty remains, however, regarding the native range of a substantial fraction of non-indigenous seaweeds in the study area. In so far as analyses of first detections can serve as a proxy for the introduction rate of non-indigenous seaweeds, these do not reveal a decrease in the introduction rate, indicating that the current measures and policies are insufficient to battle the introduction and spread of non-indigenous species in the study area.
AB - Effective monitoring of non-indigenous seaweeds and combatting their effects relies on a solid confirmation of the non-indigenous status of the respective species. We critically analysed the status of presumed non-indigenous seaweed species reported from the Mediterranean Sea, the Northeast Atlantic Ocean and Macaronesia, resulting in a list of 140 species whose non-indigenous nature is undisputed. For an additional 87 species it is unclear if they are native or non-indigenous (cryptogenic species) or their identity requires confirmation (data deficient species). We discuss the factors underlying both taxonomic and biogeographic uncertainties and outline recommendations to reduce uncertainty about the non-indigenous status of seaweeds. Our dataset consisted of over 19,000 distribution records, half of which can be attributed to only five species (Sargassum muticum, Bonnemaisonia hamifera, Asparagopsis armata, Caulerpa cylindracea and Colpomenia peregrina), while 56 species (40%) are recorded no more than once or twice. In addition, our analyses revealed considerable variation in the diversity of non-indigenous species between the geographic regions. The Eastern Mediterranean Sea is home to the largest fraction of non-indigenous seaweed species, the majority of which have a Red Sea or Indo-Pacific origin and have entered the Mediterranean Sea mostly via the Suez Canal. Non-indigenous seaweeds with native ranges situated in the Northwest Pacific make up a large fraction of the total in the Western Mediterranean Sea, Lusitania and Northern Europe, followed by non-indigenous species with a presumed Australasian origin. Uncertainty remains, however, regarding the native range of a substantial fraction of non-indigenous seaweeds in the study area. In so far as analyses of first detections can serve as a proxy for the introduction rate of non-indigenous seaweeds, these do not reveal a decrease in the introduction rate, indicating that the current measures and policies are insufficient to battle the introduction and spread of non-indigenous species in the study area.
KW - Biodiversity
KW - Chlorophyta
KW - Europe
KW - Phaeophyceae
KW - Rhodophyta
KW - invasive alien species
KW - non-indigenous species
UR - https://www.scopus.com/pages/publications/85185469975
U2 - 10.1080/09670262.2023.2256828
DO - 10.1080/09670262.2023.2256828
M3 - Article
AN - SCOPUS:85185469975
SN - 0967-0262
VL - 59
SP - 127
EP - 156
JO - European Journal of Phycology
JF - European Journal of Phycology
IS - 2
ER -