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Record of the non-indigenous species Sternaspis aff. nana Zhadan, Tzetlin & Salazar-Vallejo, 2017 (Annelida: Sternaspidae) in the Southwest Atlantic Ocean

Abstract

The introduction of non-indigenous marine species in new habitats is generally associated with ships arriving at ports, driven by species transported in ballast water and sediment and biofouling communities on ship hulls, drifting object and underwater surfaces in dock areas. The present paper reports the record of the specie Sternaspis aff. nana in the Atlantic Ocean, discussing its possible conservation status and method of arrival to Brazil. Sediments samples were collected in the external area (11 m depth) of the Suape Harbor (Brazil) in February 2018. Two individuals of Sternaspis aff. nana were recorded, representing the first record of this species in the Southwest Atlantic Ocean. The way S. aff. nana arrived in Brazilian waters cannot be easily determined, the short-lived lecithotrophic larvae of sternaspids suggest that the specimens found in Suape have arrived in ballast sediment. An increase in trade between Brazil and Asian countries since the 2000s has led to that more ships coming from China having arrived in Brazilian harbors. The arrival of S. aff. nana, originally described in the South China Sea, in the Suape harbor area may have resulted from this intense movement of ships between China and Brazil.

Keywords.
Polychaeta; Exotic species; Northeastern Brazil; Shipping activities; Ballast sediment

INTRODUCTION

The introduction of non-indigenous species (NIS) may cause significant ecological impacts (Carlton, 1999Carlton, J.T. 1999. The scale and ecological consequences of biological invasions in the world’s oceans. In: Sandlund, O.T.; Schei, P.J. & Viken, A. Invasive species and biodiversity management. Dordrecht, Kluwer Academic Publishers. p. 195-212.; Çinar, 2013Çinar, M.E. 2013. Alien polychaete species worldwide: current status and their impacts. Journal of the Marine Biological Association of the United Kingdom, 93(5): 1257-1278. http://doi.org/10.1017/S0025315412001646
http://doi.org/10.1017/S0025315412001646...
), being these introductions generally associated with ships arriving at ports (Bumbeer & Rocha, 2016Bumbeer, J. & Rocha, R.M. 2016. Invading the natural marine substrates: a case study with invertebrates in South Brazil. Zoologia, 33(3): 1-7, e20150211. http://doi.org/10.1590/S1984-4689zool-20150211
http://doi.org/10.1590/S1984-4689zool-20...
), driven by species associated with ballast water/sediment and biofouling communities on ship hulls, drifting object and underwater surfaces in dock areas (Keppel et al., 2015Keppel, E.; Tovar-Hernández, M.A.; Ruiz, G. 2015. First record and establishment of Branchiomma coheni (Polychaeta: Sabellidae) in the Atlantic Ocean and review of non-indigenous species of the genus. Zootaxa, 4058: 499-518.). Benthic invertebrates have a wide variety of life histories (Godwin, 2003Godwin, L.S. 2003. Hull fouling of maritime vessels as a pathway for marine species invasions to the Hawaiian Islands. Biofouling, 19: 123-131. http://doi.org/10.1080/0892701031000061750
http://doi.org/10.1080/08927010310000617...
) and many have long larval stages, favoring transport of these species between areas separated by thousands of kilometers (Townsend et al., 2006Townsend, M.; Worsfold, T.M.; Smith, P.R.J.; Martina, L.J.; McNeill, C.L. & Kendall, M.A. 2006. Occurrence of Sternaspis scutata (Polychaeta: Sternaspidae) in the English Channel. Cahiers de Biologie Marine, 47: 281-285. http://doi.org/10.21411/CBM.A.C5023B39
http://doi.org/10.21411/CBM.A.C5023B39...
; Çinar, 2013Çinar, M.E. 2013. Alien polychaete species worldwide: current status and their impacts. Journal of the Marine Biological Association of the United Kingdom, 93(5): 1257-1278. http://doi.org/10.1017/S0025315412001646
http://doi.org/10.1017/S0025315412001646...
). Even benthic species without planktonic stage or with short-lived larvae can efficiently disperse using different ways of transportation (Jablonsky & Lutz, 1983Jablonsky, D. & Lutz, R.A. 1983. Larval ecology of marine benthic invertebrates: Paleobiological implications. Biological Reviews, 58: 21-89. http://doi.org/10.1111/j.1469-185X.1983.tb00380.x
http://doi.org/10.1111/j.1469-185X.1983....
; Winston, 2012Winston, J. 2012. Dispersal in marine organisms without a pelagic larval phase. Integrative and Comparative Biology, 52(4): 447-57. http://doi.org/10.1093/icb/ics040
http://doi.org/10.1093/icb/ics040...
), such as drifting, rafting, hitchhiking, creeping, and hopping (Thiel & Haye, 2006Thiel, M. & Haye, P.A. 2006. The ecology of rafting in the marine environment. III. Biogeographical and evolutionary consequences. Oceanography and Marine Biology: An Annual Review, 44: 323-429.; Winston, 2012Winston, J. 2012. Dispersal in marine organisms without a pelagic larval phase. Integrative and Comparative Biology, 52(4): 447-57. http://doi.org/10.1093/icb/ics040
http://doi.org/10.1093/icb/ics040...
).

The number of NIS has increased concomitantly with the increase of transoceanic transport (Keppel et al., 2015Keppel, E.; Tovar-Hernández, M.A.; Ruiz, G. 2015. First record and establishment of Branchiomma coheni (Polychaeta: Sabellidae) in the Atlantic Ocean and review of non-indigenous species of the genus. Zootaxa, 4058: 499-518.), since the shipping transport is considered the main vector of marine species invasions worldwide (Gollasch et al., 2002Gollasch, S.; Macdonald, E.; Belson, S.; Botnen, H.; Christensen, J.; Hamer, J.; Houvenaghel, G.; Jelmert, A.; Lucas, I.; Masson, D.; McCollin, T.; Olenin, S.; Persson, A.; Wallentinus, I.; Wetsteyn, B. & Wittling, T. 2002. Life in ballast tanks. In: Leppäkoski E.; Gollasch, S. & Olenin, S. Invasive aquatic species of Europe: distribution, impacts and management. Dordrecht, Kluwe., p. 217-231.; Çinar, 2013Çinar, M.E. 2013. Alien polychaete species worldwide: current status and their impacts. Journal of the Marine Biological Association of the United Kingdom, 93(5): 1257-1278. http://doi.org/10.1017/S0025315412001646
http://doi.org/10.1017/S0025315412001646...
; Gollasch & David, 2019Gollasch, S. & David, M. 2019. Ballast Water: Problems and Management. In: Sheppard, C. World Seas: An Environmental Evaluation. Academic Press, New York, 237-250.) and it can lead to a profound alteration of the diversity and structure of coastal communities (Carlton, 1999Carlton, J.T. 1999. The scale and ecological consequences of biological invasions in the world’s oceans. In: Sandlund, O.T.; Schei, P.J. & Viken, A. Invasive species and biodiversity management. Dordrecht, Kluwer Academic Publishers. p. 195-212.; Hamer, 2002Hamer, J.P. 2002. Ballast Tank Sediments. In: Leppäkoski E.; Gollasch S. & Olenin S. (Eds.). Invasive Aquatic Species of Europe. Distribution Impacts and Management. Dordrecht, Springer. p. 232-257. http://doi.org/10.1007/978-94-015-9956-6_24
http://doi.org/10.1007/978-94-015-9956-6...
; Çinar, 2013Çinar, M.E. 2013. Alien polychaete species worldwide: current status and their impacts. Journal of the Marine Biological Association of the United Kingdom, 93(5): 1257-1278. http://doi.org/10.1017/S0025315412001646
http://doi.org/10.1017/S0025315412001646...
). Carlton (1999Carlton, J.T. 1999. The scale and ecological consequences of biological invasions in the world’s oceans. In: Sandlund, O.T.; Schei, P.J. & Viken, A. Invasive species and biodiversity management. Dordrecht, Kluwer Academic Publishers. p. 195-212.) estimated that a 17th century wooden vessel could easily have transported 150 species of marine protists, invertebrates and plants per voyage, a number that may be rivalled or exceeded by a 21th century ship due to faster transit times and larger hull sizes. Ahyong et al. (2020Ahyong, S.; Costello, M.J.; Galil, B.S.; Gollasch, S.; Hutchings, P.; Katsanevakis, S.; Lejeusne, C.; Marchini, A.; Occhipinti, A.; Pagad, S.; Poore, G.; Rius, M.; Robinson, T.B.; Sterrer, W.; Turon, X.; Willan, R.C. & Zhan, A. 2020. World Register of Introduced Marine Species (WRiMS). Available: Available: http://www.marinespecies.org/introduced . Access: 18/09/2020.
http://www.marinespecies.org/introduced...
) recorded more than 1.737 marine alien species globally. Most were probably introduced by ship movements (ballast tanks and/or biofouling) (Ruiz, 1997Ruiz, G.M.; Carlton, J.T.; Grosholz, E.D. & Hines, A.H. 1997. Global invasions of marine and estuarine habitats by non-indigenous species: mechanisms, extent, and consequences. American Zoologist, 37(6): 619-630. http://doi.org/10.1093/icb/37.6.621
http://doi.org/10.1093/icb/37.6.621...
; Godwin, 2003Godwin, L.S. 2003. Hull fouling of maritime vessels as a pathway for marine species invasions to the Hawaiian Islands. Biofouling, 19: 123-131. http://doi.org/10.1080/0892701031000061750
http://doi.org/10.1080/08927010310000617...
; Seebens et al., 2013Seebens, H.; Gastner, M.T. Blasius, B. & Courchamp, F. 2013. The risk of marine bioinvasion caused by global shipping. Ecology letters, 16(6): 782-790. http://doi.org/10.1111/ele.12111
http://doi.org/10.1111/ele.12111...
). More than 292 species of marine polychaetes, belonging to 164 genera, have been reported as NIS globally, most of them Syllidae Grube, 1850, Spionidae Grube, 1850, Sabellidae Latreille, 1825, Serpulidae Rafinesque, 1815 and Nereididae Blainville, 1818 (Çinar, 2013Çinar, M.E. 2013. Alien polychaete species worldwide: current status and their impacts. Journal of the Marine Biological Association of the United Kingdom, 93(5): 1257-1278. http://doi.org/10.1017/S0025315412001646
http://doi.org/10.1017/S0025315412001646...
). Among the approximately 46 polychaeta species classified as NIS in Brazil (Rodrigues et al., 2020Rodrigues, A.R.; Skinner, L.F. & Brasil, A.C.D.S. 2020. Do Morphological Similarities and human-induced dispersal explain the non-native occurrence of Serpulidae (Annelida) in Southwest Atlantic? Taxonomic detailing is the key. Papéis Avulsos de Zoologia, 60(5): 1-15, e20206005. http://doi.org/10.11606/1807-0205/2020.60.05
http://doi.org/10.11606/1807-0205/2020.6...
), eight are invasive exotic species (I3N, 2018Invasives Information Network (I3N) 2018. Base de dados nacional de espécies exóticas invasoras - Brasil. Available: Available: http://i3n.institutohorus.org.br/www . Access: 01/05/2019.
http://i3n.institutohorus.org.br/www...
). To date, non-indigenous Sternaspidae has not been recorded on the Brazilian coast, but in the UK (Townsend et al., 2006Townsend, M.; Worsfold, T.M.; Smith, P.R.J.; Martina, L.J.; McNeill, C.L. & Kendall, M.A. 2006. Occurrence of Sternaspis scutata (Polychaeta: Sternaspidae) in the English Channel. Cahiers de Biologie Marine, 47: 281-285. http://doi.org/10.21411/CBM.A.C5023B39
http://doi.org/10.21411/CBM.A.C5023B39...
; Shelley et al., 2008Shelley, R.; Widdicombe, S.; Woodward, M.; Stevens, T.; McNeill, C.L.; & Kendall, M.A. 2008. An investigation of the impacts on biodiversity and ecosystem functioning of soft sediments by the non-native polychaete Sternaspis scutata (Polychaeta: Sternaspidae). Journal of Experimental Marine Biology and Ecology, 366(1-2), 146-150. http://doi.org/10.1016/j.jembe.2008.07.018
http://doi.org/10.1016/j.jembe.2008.07.0...
), India (Jose et al., 2014Jose, H.P.M.; Muthuvelu, S.; Sivaraj, S. & Murugesan, P. 2014. A Note on the Occurrence of Sternaspis scutata (Renier 1807) - A Sternaspid Polychaete from Sundarban Mangroves, West Bengal, India. Journal of the Bombay Natural History Society (JBNHS), 111(1): 62-64. http://doi.org/10.17087/bnhs/2014/v111i1/56547
http://doi.org/10.17087/bnhs/2014/v111i1...
) and Egypt (Abdelnaby, 2020Abdelnaby, A.F. 2020. First record of Sternaspis scutata (Polychaeta, Sternaspidae) in Egyptian waters. Egyptian Journal of Aquatic Biology and Fisheries, 24(2), 317-326. http://doi.org/10.21608/EJABF.2020.85232
http://doi.org/10.21608/EJABF.2020.85232...
), Sternaspis scutata (Ranzani, 1817Ranzani, C. 1817. Descrizione di una nuova specie del genere Thalassema. Opuscoli scientifica, 2(112): 12-13.) has been recorded as a non-native or invasive polychaeta.

Sternaspids are polychaetes with a peanut-shaped body and a characteristic stiff ventral shield (Sendall & Salazar-Vallejo, 2013Sendall, K. & Salazar-Vallejo, S.I. 2013. Revision of Sternaspis Otto, 1821 (Polychaeta, Sternaspidae). ZooKeys, 286: 1-74. http://doi.org/10.3897/zookeys.286.4438
http://doi.org/10.3897/zookeys.286.4438...
). Up to date, 44 species of Sternaspidae Carus, 1863Carus, J.V. 1863. Vermes. In: Peters, W.C.H.; Carus, J.V. & Gerstäcker, C.E.A. Handbuch der Zoologie. Leipzig, Wilhelm Engelmann. v. 2, p. 422-484. http://biodiversitylibrary.org/page/1092677.
http://biodiversitylibrary.org/page/1092...
have been recorded in marine waters worldwide (Sendall & Salazar-Vallejo, 2013Sendall, K. & Salazar-Vallejo, S.I. 2013. Revision of Sternaspis Otto, 1821 (Polychaeta, Sternaspidae). ZooKeys, 286: 1-74. http://doi.org/10.3897/zookeys.286.4438
http://doi.org/10.3897/zookeys.286.4438...
; Díaz-Díaz & Rozbaczylo, 2017Díaz-Díaz, O. & Rozbaczylo, N. 2017. Sternaspis chilensis n. sp., a new species from austral Chilean channels and fjords (Annelida, Sternaspidae). Zootaxa, 4254(2): 269-276.; Fiege & Barnich, 2020Fiege, D. & Barnich, R. 2020. A new genus and species of Sternaspidae (Annelida: Polychaeta) from the deep eastern Atlantic. European Journal of Taxonomy, 699: 1-13.). The family has four genera: SternaspisOtto, 1820Otto, A.G. 1820. De Sternaspide thalassemoideo et Siphostomate diplochaito vermibus duobus marinis. Vratislaviae, Typis Universitatis., CaulleryaspisSendall & Salazar-Vallejo, 2013Sendall, K. & Salazar-Vallejo, S.I. 2013. Revision of Sternaspis Otto, 1821 (Polychaeta, Sternaspidae). ZooKeys, 286: 1-74. http://doi.org/10.3897/zookeys.286.4438
http://doi.org/10.3897/zookeys.286.4438...
, PetersenaspisSendall & Salazar-Vallejo, 2013Sendall, K. & Salazar-Vallejo, S.I. 2013. Revision of Sternaspis Otto, 1821 (Polychaeta, Sternaspidae). ZooKeys, 286: 1-74. http://doi.org/10.3897/zookeys.286.4438
http://doi.org/10.3897/zookeys.286.4438...
and MauretanaspisFiege & Barnich, 2020Fiege, D. & Barnich, R. 2020. A new genus and species of Sternaspidae (Annelida: Polychaeta) from the deep eastern Atlantic. European Journal of Taxonomy, 699: 1-13., distinguished via characteristics of the shield, introvert hooks and the number of segments of the anterior portion of abdomen (Sendall & Salazar-Vallejo, 2013Sendall, K. & Salazar-Vallejo, S.I. 2013. Revision of Sternaspis Otto, 1821 (Polychaeta, Sternaspidae). ZooKeys, 286: 1-74. http://doi.org/10.3897/zookeys.286.4438
http://doi.org/10.3897/zookeys.286.4438...
; Drennan et al., 2019Drennan, R.; Wiklund, H.; Rouse, G.W.; Georgieva, M.N.; Wu, X.; Kobayashi, G.; Yoshino, K. & Glover, A.G. 2019. Taxonomy and phylogeny of mud owls (Annelida: Sternaspidae), including a new synonymy and new records from the Southern Ocean, North East Atlantic Ocean and Pacific Ocean: challenges in morphological delimitation. Marine Biodiversity, 49: 2659-2697.).

Common and occurring in all oceans, sternaspids are motile, subsurface deposit feeders and are observed in association with a great variety of substrates ranging from coarse sand to soft mud (Sendall & Salazar-Vallejo, 2013Sendall, K. & Salazar-Vallejo, S.I. 2013. Revision of Sternaspis Otto, 1821 (Polychaeta, Sternaspidae). ZooKeys, 286: 1-74. http://doi.org/10.3897/zookeys.286.4438
http://doi.org/10.3897/zookeys.286.4438...
; Jumars et al., 2015Jumars, P.A.; Dorgan, K.M. & Lindsey, S.M. 2015. Diet of worms emended: an update of polychaete feeding guilds. Annual Review of Marine Sciences, 7: 497-520. http://doi.org/10.1146/annurev-marine-010814-020007
http://doi.org/10.1146/annurev-marine-01...
; Díaz-Díaz & Rozbaczylo, 2017Díaz-Díaz, O. & Rozbaczylo, N. 2017. Sternaspis chilensis n. sp., a new species from austral Chilean channels and fjords (Annelida, Sternaspidae). Zootaxa, 4254(2): 269-276.). The high adaptive capacity of sternaspids can favor introductions of these polychaetes in non-native environments, but only Sternaspis scutata has already been registered as invasive especie (Townsend et al., 2006Townsend, M.; Worsfold, T.M.; Smith, P.R.J.; Martina, L.J.; McNeill, C.L. & Kendall, M.A. 2006. Occurrence of Sternaspis scutata (Polychaeta: Sternaspidae) in the English Channel. Cahiers de Biologie Marine, 47: 281-285. http://doi.org/10.21411/CBM.A.C5023B39
http://doi.org/10.21411/CBM.A.C5023B39...
) in European waters.

Only Petersenaspis capillata (Nonato, 1966Nonato, E.F. 1966. Sternaspis capillata sp. n. (Annelida, Polychaeta). Boletim do Instituto Oceanográfico da Universidade de São Paulo, 15(1): 79-83. http://doi.org/10.1590/S0373-55241966000100011
http://doi.org/10.1590/S0373-55241966000...
) has been recorded in Brazil, occurring from Pernambuco to Rio Grande do Sul, in muddy bottoms ranging from shallow waters (estuaries and beaches) to the deep sea (Amaral et al., 2013Amaral, A.C.Z.; Nallin, S.A.H.; Steiner, T.M.; Forroni, T.O. & Gomes, D.F. 2013. Catálogo das espécies de Annelida Polychaeta do Brasil. Available: Available: http://www.ib.unicamp.br/museu_zoologia/files/lab_museu_zoologia/Catalogo_Polychaeta_Amaral_et_al_2012.pdf . Access: 01/09/2020.
http://www.ib.unicamp.br/museu_zoologia/...
). Sternaspis nanaZhadan et al., 2017Zhadan, A.E.; Tzetlin, A.B. & Salazar-Vallejo, S.I. 2017. Sternaspidae (Annelida, Sedentaria) from Vietnam with description of three new species and clarification of some morpho logical features. Zootaxa, 4226: 75-92. http://doi.org/10.11646/zootaxa.4226.1.3
http://doi.org/10.11646/zootaxa.4226.1.3...
was recently described in the South China Sea. We present the record of Sternaspis aff. Nana in the Southwest Atlantic Ocean, discussing its possible ‘conservation status’ and method of arrival in Brazil.

MATERIAL AND METHODS

Sediments samples were collected in the external area of the Suape Harbor (Pernambuco, Brazil - 08°23′37.6″S 34°57′19.3″W) in February 2018. Samples were collected using a Van Veen Grab at a depth of 15 m. After collection, samples were fixed in saline formalin 4% and thereafter the polychaetes were identified following Zhadan et al. (2017Zhadan, A.E.; Tzetlin, A.B. & Salazar-Vallejo, S.I. 2017. Sternaspidae (Annelida, Sedentaria) from Vietnam with description of three new species and clarification of some morpho logical features. Zootaxa, 4226: 75-92. http://doi.org/10.11646/zootaxa.4226.1.3
http://doi.org/10.11646/zootaxa.4226.1.3...
). After identification, all specimens were deposited in the “Museu de Oceanografia Prof. Petrônio Alves Coelho (MOUFPE)” at Universidade Federal de Pernambuco, Recife, Brazil.

RESULTS

Systematics

Order Terebellida Rouse & Fauchald, 1997Rouse, G.W. & Fauchald, K. 1997. Cladistics and polychaetes. Zoologica Scripta, 26(2): 139-204.

Family Sternaspidae Carus, 1863Carus, J.V. 1863. Vermes. In: Peters, W.C.H.; Carus, J.V. & Gerstäcker, C.E.A. Handbuch der Zoologie. Leipzig, Wilhelm Engelmann. v. 2, p. 422-484. http://biodiversitylibrary.org/page/1092677.
http://biodiversitylibrary.org/page/1092...

Genus Sternaspis Otto, 1820Otto, A.G. 1820. De Sternaspide thalassemoideo et Siphostomate diplochaito vermibus duobus marinis. Vratislaviae, Typis Universitatis.

Sternaspis aff. Nana Zhadan et al., 2017 Zhadan, A.E.; Tzetlin, A.B. & Salazar-Vallejo, S.I. 2017. Sternaspidae (Annelida, Sedentaria) from Vietnam with description of three new species and clarification of some morpho logical features. Zootaxa, 4226: 75-92. http://doi.org/10.11646/zootaxa.4226.1.3
http://doi.org/10.11646/zootaxa.4226.1.3...

(Figs. 1-3)

Figure 1
Sternaspis aff. Nana collected in Suape Harbor (Pernambuco, Brazil). (A) Ventral view. White arrows showing genital papillae; (B) Dorsal view; (C) Detailed ventral view of abdomen (pre-shield). Black arrows showing long filiform papillae and white arrows showing genital papillae.

Figure 2
Sternaspis aff. nana collected in Suape Harbor (Pernambuco, Brazil). (A) Detailed view of the margin of abdomen wall. White arrows showing pre-shield capillary chaetae; (B) Ventrocaudal shields. Black dotted showing shield plates nearly square. White arrows showing fascicles containing only one thick chaeta each, black arrow showing fan corners extended.

Figure 3
Sternaspis aff. nana collected in Suape Harbor (Pernambuco, Brazil). Detail of Introvert hooks of the first chaetiger.

Sternaspis nanaZhadan et al., 2017Zhadan, A.E.; Tzetlin, A.B. & Salazar-Vallejo, S.I. 2017. Sternaspidae (Annelida, Sedentaria) from Vietnam with description of three new species and clarification of some morpho logical features. Zootaxa, 4226: 75-92. http://doi.org/10.11646/zootaxa.4226.1.3
http://doi.org/10.11646/zootaxa.4226.1.3...
: 79-82, fig. 3-5; Salazar-Vallejo, 2017Salazar-Vallejo, S.I. 2017. Six new tropical sternaspid species (Annelida, Sternaspidae) with keys to identify genera and species. Zoological Studies, 56: 32(1-16). http://doi.org/10.6620/2FZS.2017.56-32
http://doi.org/10.6620/2FZS.2017.56-32...
: 4.

Examined material

Two specimens collected at the external area of the Suape Harbor, Pernambuco, Brazil (08°23′37.6″S, 34°57′19.3″W), mud substrate, 15 m depth, 16-II-2018, MOUPFE 003.

Description

The morphology of the two specimens agree with the descriptions of Sternaspis nana by Zhadan et al. (2017Zhadan, A.E.; Tzetlin, A.B. & Salazar-Vallejo, S.I. 2017. Sternaspidae (Annelida, Sedentaria) from Vietnam with description of three new species and clarification of some morpho logical features. Zootaxa, 4226: 75-92. http://doi.org/10.11646/zootaxa.4226.1.3
http://doi.org/10.11646/zootaxa.4226.1.3...
), but due to the impossibility of observing the gametes due to the small size of the specimens, the morphological differences of the shield and the amount of papillae in the species found here in Brazil, we classify the specimens as Sternaspis aff. nana. Our specimens seem to be more rugose than the type specimens and the posterior shield margin has a round projection, as opposed to having a sharp one, or none as in the type species (Zhadan et al., 2017Zhadan, A.E.; Tzetlin, A.B. & Salazar-Vallejo, S.I. 2017. Sternaspidae (Annelida, Sedentaria) from Vietnam with description of three new species and clarification of some morpho logical features. Zootaxa, 4226: 75-92. http://doi.org/10.11646/zootaxa.4226.1.3
http://doi.org/10.11646/zootaxa.4226.1.3...
).

Complete specimens with 26 segments without clear borders (Body: 2.20 mm long, 0.82 mm wide). Body hourglass-shaped, introvert narrower than abdomen, constriction between segments 5 and 6. Body wall semi-transparent; introvert colorless, abdomen creamish-white with abundant minute papillae evenly distributed, both dorsally and ventrally, and papillae cirriform (Fig. 1C). Intestine and ventral nerve are visible through body wall (Figs. 1A-B, 2B).

First three chaetigers with 13 falcate hooks per bundle, not subdistally expanded, hooks transparent (Fig. 3). Genital papilla small, digitate, protruding ventrally from sixth chaetiger (Fig. 1A, C). Pre-shield region with 7 segments, with 1-2 fine capillary chaetae laterally in some segments (Fig. 2A).

Ventrocaudal shield soft, smooth, papillae not observed and no sediment particles attached. Left shield plate 0.21 mm long, 0.25 mm wide. Shield plates nearly square. Ribs and concentric lines not visible. (Fig. 2B). No visible borders between lateral plates and fan (Fig. 2B). Anterior keels visible, suture well-defined, visible throughout shield (Fig. 2B).

Bundles of shield chaetae with eight lateral shield chaetae, ovally arranged and five posterior fascicles each containing only one thick chaeta, slightly curved (Fig. 2B). Peg-chaetae not observed. Branchial filaments arranged in discrete branchial plates.

Distribution

Type locality: Pacific Ocean - Nha Trang Bay, South China Sea (15-40 m depth). New occurrence: Atlantic Ocean - Suape Harbor Area, Pernambuco, Brazil (15 m depth).

Remarks

On the Brazilian coast, only one species of Sternaspidae has been recorded to date, Petersenaspis capillata (Nonato, 1966Nonato, E.F. 1966. Sternaspis capillata sp. n. (Annelida, Polychaeta). Boletim do Instituto Oceanográfico da Universidade de São Paulo, 15(1): 79-83. http://doi.org/10.1590/S0373-55241966000100011
http://doi.org/10.1590/S0373-55241966000...
) [= Sternaspis capillata Nonato, 1966], which is native and found in Brazilian waters (Nonato, 1966Nonato, E.F. 1966. Sternaspis capillata sp. n. (Annelida, Polychaeta). Boletim do Instituto Oceanográfico da Universidade de São Paulo, 15(1): 79-83. http://doi.org/10.1590/S0373-55241966000100011
http://doi.org/10.1590/S0373-55241966000...
). The morphology of our specimens is similar to the original description of Sternaspis nana by Zhadan et al. (2017Zhadan, A.E.; Tzetlin, A.B. & Salazar-Vallejo, S.I. 2017. Sternaspidae (Annelida, Sedentaria) from Vietnam with description of three new species and clarification of some morpho logical features. Zootaxa, 4226: 75-92. http://doi.org/10.11646/zootaxa.4226.1.3
http://doi.org/10.11646/zootaxa.4226.1.3...
) and resembles S. papillosaZhadan et al., 2017Zhadan, A.E.; Tzetlin, A.B. & Salazar-Vallejo, S.I. 2017. Sternaspidae (Annelida, Sedentaria) from Vietnam with description of three new species and clarification of some morpho logical features. Zootaxa, 4226: 75-92. http://doi.org/10.11646/zootaxa.4226.1.3
http://doi.org/10.11646/zootaxa.4226.1.3...
and S. africanaAugener, 1918Augener, H. 1918. Polychaeta. In: Beiträge zur Kenntnis des Meeresfauna Westafrikas, Hamburg, L. Friederischen. v. 2, pt. 2, p. 2, p. 67-625, 6 pl.. Sternaspis aff. nana markedly differs from these species by combined features related to hooks of introvert, papillae pattern and ventral shield characteristics.

In S. aff. nana there are 13 falcate hooks per bundle in the introvert chaetigers, while the number of falcate hooks per bundle is 16 in S. papillosa and 15-20 in S. africana. Sternaspis aff. nana has abundant micropapillae and regular rows of long cirriform papillae along the body. In S. papillosa digitiform papillae are organized in more or less regular transverse rows, and in S. africana minute papillae are densely present on segments 7 and 8, but evenly spaced in other segments. Ventral shield in S. aff. nana is without ribs and papillae, usually without concentric lines, with eight lateral shield chaetae in oval pattern, and six posterior shield chaetae consisting of a single thick chaeta in slightly curved pattern. In S. papillosa, ventral shield is with underdeveloped ribs and concentric lines, covered by fine papillae, with nine lateral shield chaetae in oval pattern, and five posterior shield chaetae in oval pattern; in S. Africana, ventral shield is with ribs and concentric lines barely visible, without papillae, with nine lateral shield chaetae in oval pattern, and five posterior shield chaetae in slightly curved pattern. The morphological features remarks are resumed in Table 1.

Table 1
Main morphological features of Sternaspis aff. nana, S. africana, S. papillosa. Legend: BP (Body papillae), IH (Introvert Hooks), CBW (Chaetae of body wall), S (Shield), LSC (Laterial shield chaetae), PSC (Posterior shield chaetae), PC (Peg Chaetae).

DISCUSSION

The polychaete Sternaspis nana was originally described in the South China Sea at depths ranging from 15-40 m in muddy substrates (Zhadan et al., 2017Zhadan, A.E.; Tzetlin, A.B. & Salazar-Vallejo, S.I. 2017. Sternaspidae (Annelida, Sedentaria) from Vietnam with description of three new species and clarification of some morpho logical features. Zootaxa, 4226: 75-92. http://doi.org/10.11646/zootaxa.4226.1.3
http://doi.org/10.11646/zootaxa.4226.1.3...
). This is the first record of this species on the Brazil coast, expanding the known geographic distribution of S. aff. nana to the Southwest Atlantic Ocean and indicating the occurrence of a new non-indigenous species (NIS) for the Brazilian waters.

Studies have shown that the occurrence of some organisms could not be explained by the natural distribution of larvae and/or adults (Farrapeira et al., 2011Farrapeira, C.M.R.; Tenório, D.O. & Amaral, F.D. 2011. Vessel biofouling as an inadvertent vector of benthic invertebrates occurring in Brazil. Marine Pollution Bulletin, 62(4): 832-839.). The shipping industry, via ballast water and sediments, anchoring, and biofouling, may be the main vector of marine species introduction, including polychaetes (Neves & Rocha, 2008Neves, C.S. & Rocha, R.M. 2008. Introduced and cryptogenic species and their management in Paranaguá Bay, Brazil. Brazilian Archives of Biology and Technology, 51(3): 623-633. http://doi.org/10.1590/S1516-89132008000300025
http://doi.org/10.1590/S1516-89132008000...
; Çinar, 2013Çinar, M.E. 2013. Alien polychaete species worldwide: current status and their impacts. Journal of the Marine Biological Association of the United Kingdom, 93(5): 1257-1278. http://doi.org/10.1017/S0025315412001646
http://doi.org/10.1017/S0025315412001646...
; Gollasch & David, 2019Gollasch, S. & David, M. 2019. Ballast Water: Problems and Management. In: Sheppard, C. World Seas: An Environmental Evaluation. Academic Press, New York, 237-250.). Introduction of NIS by commercial shipping typically results in harbors becoming hotspots of biotic invasion (Wasson et al., 2001Wasson, K.; Zabin, C.J.; Bedinger, L.; Diaz, M.C. & Pearse, J.S. 2001. Biological invasions of estuaries without international shipping: the importance of intraregional transport. Biological conservation, 102(2): 143-153. http://doi.org/10.1016/S0006-3207(01)00098-2
http://doi.org/10.1016/S0006-3207(01)000...
; Hewitt et al., 2004Hewitt, C.L.; Campbell, M.L.; Thresher, R.E.; Martin, R.B.; Boyd, S.; Cohen, B.F.; Currie, D.R.; Gomon, M.F.; Keough, M.J.; Lewis, J.A.; Lockett, M.M.; Mays, N.; McArthur, M.A.; O’Hara, T.D.; Poore, G.C.B.; Ross, D.J.; Storey, M.J.; Watson, J.E. & Wilson, R.S. 2004. Introduced and cryptogenic species in port Phillip bay, Victoria, Australia. Marine Biology, 144(1): 183-202. http://doi.org/10.1007/s00227-003-1173-x
http://doi.org/10.1007/s00227-003-1173-x...
). Globally, about 1.697 species are classified as alien species, 78 species with uncertain origin and 121 species with unknown origin (Ahyong et al., 2020Ahyong, S.; Costello, M.J.; Galil, B.S.; Gollasch, S.; Hutchings, P.; Katsanevakis, S.; Lejeusne, C.; Marchini, A.; Occhipinti, A.; Pagad, S.; Poore, G.; Rius, M.; Robinson, T.B.; Sterrer, W.; Turon, X.; Willan, R.C. & Zhan, A. 2020. World Register of Introduced Marine Species (WRiMS). Available: Available: http://www.marinespecies.org/introduced . Access: 18/09/2020.
http://www.marinespecies.org/introduced...
). In Brazil, around 46% of recorded marine NIS were introduced by ballast water/sediments and/or biofouling (Lopes et al., 2009Lopes, R.; Coradin, L.; Pombo, V.B. & Cunha, D.R. 2009. Informe sobre as espécies exóticas invasoras marinhas no Brasil. Brasília, MMA). Farrapeira et al. (2011Farrapeira, C.M.R.; Tenório, D.O. & Amaral, F.D. 2011. Vessel biofouling as an inadvertent vector of benthic invertebrates occurring in Brazil. Marine Pollution Bulletin, 62(4): 832-839.) cite that introduction by hull biofouling has been proven for 228 species of marine invertebrates. Polychaetes such as Branchiomma luctuosum (Grube, 1870Grube, E. 1870. Beschreibungen neuer oder weniger bekannter von Hrn. Ehrenberg gesammelter Anneliden des rothen Meeres. Monatsberichte der Koniglichen Preussischen Akademie der Wissenschaften Berlin, 1869: 484-521.) (original distribution: Red Sea; Nogueira et al., 2006Nogueira, J.M.M.; Rossi, M.C.S. & Lopez, E. 2006. Intertidal species of Branchiomma Kölliker and Pseudobranchiomma Jones (Polychaeta: Sabellidae: Sabellinae) occurring on rocky shores along the state of São Paulo, Southeastern Brazil. Zoological Studies, 45(4): 586-610.; Oricchio et al., 2019Oricchio, F.T.; Marques, A.C.; Hajdu, E.; Pitombo, F.B.; Azevedo, F.; Passos, F.D.; Vieira, L.M.; Stampar, S.N.; Rocha, R.M. & Dias, G.M. 2019. Exotic species dominate marinas between the two most populated regions in the southwestern Atlantic Ocean. Marine Pollution Bulletin, 146: 884-892. http://doi.org/10.1016/j.marpolbul.2019.07.013
http://doi.org/10.1016/j.marpolbul.2019....
), Polydora cornutaBosc, 1802Bosc, L.A.G. 1802. Histoire naturelle des vers, contenant leur déscription et leurs moeurs, avec figures dessinées d’après nature. Paris, Deterville. 3v. (original distribution: Western Atlantic and Caribbean; Neves & Rocha, 2008Neves, C.S. & Rocha, R.M. 2008. Introduced and cryptogenic species and their management in Paranaguá Bay, Brazil. Brazilian Archives of Biology and Technology, 51(3): 623-633. http://doi.org/10.1590/S1516-89132008000300025
http://doi.org/10.1590/S1516-89132008000...
), Pseudopolydora diopatraHsieh, 1992Hsieh, H.L. 1992. Pseudopolydora diopatra, a new species (Polychaeta: Spionidae) from Taiwan. Proceedings of the Biological Society of Washington, 105(3): 630-635. (original distribution: Western Pacific - Taiwan; Silva & Barros, 2011Silva, E.C. & Barros, F. 2011. Macrofauna bentônica introduzida no Brasil: Lista de espécies marinhas e dulciaquícolas e distribuição atual. Oecologia Australis, 2(15): 326-344. http://doi.org/10.4257/oeco.2011.1502.10
http://doi.org/10.4257/oeco.2011.1502.10...
), Hydroides elegans (Haswell, 1883Haswell, W.A. 1883. On some new Australian tubicolous Annelids. Proceedings of the Linnean Society of New South Wales, 7: 633-638.) (original distribution: Australasia and the Indian Ocean; Schwan et al., 2016Schwan, I.D.S.; Brasil, A.C.D.S.; Neves, D. & Dias, G.M. 2016. The invasive worm Hydroides elegans (Polychaeta-Serpulidae) in southeastern Brazil and its potential to dominate hard substrata. Marine Biology Research, 12(1): 96-103.; Oricchio et al., 2019Oricchio, F.T.; Marques, A.C.; Hajdu, E.; Pitombo, F.B.; Azevedo, F.; Passos, F.D.; Vieira, L.M.; Stampar, S.N.; Rocha, R.M. & Dias, G.M. 2019. Exotic species dominate marinas between the two most populated regions in the southwestern Atlantic Ocean. Marine Pollution Bulletin, 146: 884-892. http://doi.org/10.1016/j.marpolbul.2019.07.013
http://doi.org/10.1016/j.marpolbul.2019....
) and Trochochaeta japonicaImajima, 1989Imajima, M. 1989. A new species of Trochochaeta (Polychaeta, Trochochaetidae) from Japan. Bulletin of the National Science Museum, Tokyo, Series A (Zoology), 15(3): 139-146. (original distribution: Pacific North - Japão; Radashevsky et al., 2018Radashevsky, V.I.; Rizzo, A.E. & Peixoto, A.J. 2018. First record of Trochochaeta japonica (Annelida: Spionidae) in Brazil with identification key to species of the genus. Zootaxa, 4462(4): 566-578.) are already known to have been introduced to the Brazilian coast in ship ballast tanks and/or biofouling.

The way S. aff. nana arrived in Brazilian waters cannot be easily determined. In general, species with larvae that actively seek food (planktotrophic larvae) disperse easily and may invade new areas, although species with lecithotrophic development (that do not need external food) have also been registered as invaders (Jablonsky & Lutz, 1983Jablonsky, D. & Lutz, R.A. 1983. Larval ecology of marine benthic invertebrates: Paleobiological implications. Biological Reviews, 58: 21-89. http://doi.org/10.1111/j.1469-185X.1983.tb00380.x
http://doi.org/10.1111/j.1469-185X.1983....
). Given that sternaspids larvae are short-lived and lecithotrophic (Strathmann, 1987Strathmann, M.F. 1987. Phylum Annelida, Class Polychaeta. In: Strathmann, M.F. Reproduction and Development of Marine Invertebrates of the Northern Pacific Coast: Data and Methods for the Study of Eggs, Embryos, and Larvae. Seatle, University of Washington Press. p. 138-195.), generally settling in less than two days (Rouse & Pleijel, 2001Rouse, G.W. & Pleijel, F. 2001. Polychaetes. Oxford, Oxford University Press.), and the great distance from China to Brazil (four to seven weeks travel), the species probably did not arrive in Suape Harbor as larvae, but as juveniles or adults, however it was not possible to observe the gametes in the specimens due to their small size, and thus estimate their ages.

As discussed by Winston (2012Winston, J. 2012. Dispersal in marine organisms without a pelagic larval phase. Integrative and Comparative Biology, 52(4): 447-57. http://doi.org/10.1093/icb/ics040
http://doi.org/10.1093/icb/ics040...
) invertebrates with direct development (without planktonic stage) or with short-lived larvae (yolky nonfeeding larvae) can disperse using different ways such as drifting, rafting, hitchhiking, creeping, and hopping. Sternaspis aff. nana (larvae or adults) may have arrived in Suape in ballast tanks of ships. When a vessel takes on ballast water, sediment and the associated benthic organisms, resting stages can be taken onboard (Hamer, 2002Hamer, J.P. 2002. Ballast Tank Sediments. In: Leppäkoski E.; Gollasch S. & Olenin S. (Eds.). Invasive Aquatic Species of Europe. Distribution Impacts and Management. Dordrecht, Springer. p. 232-257. http://doi.org/10.1007/978-94-015-9956-6_24
http://doi.org/10.1007/978-94-015-9956-6...
; Gollasch et al., 2002Gollasch, S.; Macdonald, E.; Belson, S.; Botnen, H.; Christensen, J.; Hamer, J.; Houvenaghel, G.; Jelmert, A.; Lucas, I.; Masson, D.; McCollin, T.; Olenin, S.; Persson, A.; Wallentinus, I.; Wetsteyn, B. & Wittling, T. 2002. Life in ballast tanks. In: Leppäkoski E.; Gollasch, S. & Olenin, S. Invasive aquatic species of Europe: distribution, impacts and management. Dordrecht, Kluwe., p. 217-231.; Gollasch & David, 2019Gollasch, S. & David, M. 2019. Ballast Water: Problems and Management. In: Sheppard, C. World Seas: An Environmental Evaluation. Academic Press, New York, 237-250.). Suspended sediment settles to the tank bottom, providing suitable habitat for benthic organisms (Gollasch & Leppakoski 1999Gollasch, S. & Leppakoski, E. 1999. Initial risk assessment of alien species in Nordic coastal Waters. Copenhagen, Nordic Council of Ministers. 246p.; Briski et al., 2010Briski, E.; Bailey, S.A.; Cristescu, M.E. & MacIsaac, H.J. 2010. Efficacy of ‘saltwater flushing’ in protecting the Great Lakes from biological invasions by invertebrate eggs in ships’ ballast sediment. Freshwater Biology, 55(11): 2414-2424. http://doi.org/10.1111/j.1365-2427.2010.02449.x
http://doi.org/10.1111/j.1365-2427.2010....
, 2011Briski, E.; Bailey, S.A. & MacIsaac, H.J. 2011. Invertebrates and their dormant eggs transported in ballast sediments of ships arriving to the Canadian coasts and the Laurentian Great Lakes. Limnology and Oceanography, 56: 1929-1939. http://doi.org/10.4319/lo.2011.56.5.1929
http://doi.org/10.4319/lo.2011.56.5.1929...
). Lucas et al. (1999Lucas, I.A.N.; McCollin, T.A. & Hamer, J.P. 1999. Marine organism in ships ballast water. Report to Ministry for Agriculture, Fisheries and Food, UK.) found volume of sediments (mostly mud) varying from a few cm to more than 30 cm depth in ballast tanks. Williams et al. (1988Williams, R.J.; Griffiths, F.B.; Van der Wal, E.J. & Kelly, J. 1988. Cargo vessel ballast water as a vector for the transport of non-indigenous marine species. Estuarine, Coastal and Shelf Science, 26(4), 409-420.) recorded 21 taxa (crustaceans and polychaetes) in ballast sediments in ships sailing between Japan and Australia. Macroinvertebrates were found by Briski et al. (2012Briski, E.; Bailey, S.A. & MacIsaac, H.J. 2012. Invasion risk posed by macroinvertebrates transported in ships’ ballast tanks Elizabeta. Biological Indicators, 14(9): 1843-1850. 10.4319/lo.2011.56.5.1929
https://doi.org/10.4319/lo.2011.56.5.192...
) in ballast sediments of 10.4% of transoceanic ships in Canada harbors, with an average density of 2.8 individuals per tank when present. Considering that S. aff. nana occurs in muddy bottoms, it is probable that the dispersion to the Suape Habor occurred in ballast sediments.

The Suape Harbor Complex is one of Brazil’s largest and most important harbors for cargo and container operation, receiving more than 1.000 ships annually from 160 countries (SUAPE, 2019Complexo Industrial Portuário Governador Eraldo Gueiros (SUAPE). 2019. The Port of the Future. Available: Available: http://www.suape.pe.gov.br/en/port/the-port-of-the-future . Access: 01/05/2020.
http://www.suape.pe.gov.br/en/port/the-p...
). Between 2013 and 2017, cargo volume in the Suape Harbor Complex increased by 73.3% for long-haul vessels, with origins and destinations to the United States, Argentina, Germany, Holland, Mexico, China and Kuwait (MTPA, 2018Ministério dos Transportes, Portos e Aviação Civil (MTPA). 2018. Planejamento portuário. Available: Available: http://www.transportes.gov.br/images/SNP/planejamento_portuario/planos_mestres/versao_preliminar/vp25v2.pdf . Access: 01/06/2019.
http://www.transportes.gov.br/images/SNP...
). In recent years, the trade between Brazil and Asia has increased; China has become Brazil’s primary trading partner (Moore, 2009Moore, M. 2009. China overtakes the US as Brazil’s largest trading partner. The Telegraph, 9 May 2009.; The World Bank, 2014The World Bank. 2014. Implications of a changing China for Brazil: a new window of opportunity? (English). Washington, DC: World Bank Group. Available: Available: http://documents.worldbank.org/curated/en/794561468017425088/Implications-of-a-changing-China-for-Brazil-a-new-window-of-opportunity . Access: 01/06/2020.
http://documents.worldbank.org/curated/e...
) and China’s relative share in Brazilian foreign trade increased from only 2% in 2000 to close to 20% in 2015 (Dantas & Jabbour, 2016Dantas, A.T. & Jabbour, M.K. 2016. Brazil and China: an assessment of recent trade relations. Economics of Agriculture, 63(1): 313-322. http://doi.org/10.5937/ekoPolj1601313T
http://doi.org/10.5937/ekoPolj1601313T...
). This increase in trade has led to more ships from China arriving in Brazilian harbors, favoring the introduction of Chinese marine species. The arrival of Sternaspis aff. nana, originally described in the South China Sea, into the Suape harbor area is likely to be a result of this intense movement of ships between China and Brazil.

ACKNOWLEDGMENTS

We would like to thank the Diretoria de Meio Ambiente e Sustentabilidade de SUAPE - Complexo Industrial Portuário Governador Eraldo Gueiros and DBF Planejamento e Consultoria for supplying the material used and providing the necessary logistic support for this study. The authors would like thanks to Section Editor and Journal Editor for supports, and reviewers that provided valuable comments and suggestions. We also thank Dr. Sergio I. Salazar-Vallejo for valuable comments, contributions and exchanging information regarding the specimen. We also thank Dr. Anna E. Zhadan for exchanging information regarding the specimen. We are also grateful to Claudeilton Santana for the help in obtaining photographs.

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  • FUNDING DECLARATION

    Authors received no specific funding for this work.
  • ETHICS AND PERMITS

    All research pertaining to this article did not require any research permits.
  • Published with the financial support of the "Programa de Apoio às Publicações Científicas Periódicas da USP"

Edited by

Edited by: Marcelo Veronesi Fukuda

Data availability

Data citations

Invasives Information Network (I3N) 2018. Base de dados nacional de espécies exóticas invasoras - Brasil. Available: Available: http://i3n.institutohorus.org.br/www Access: 01/05/2019.

Publication Dates

  • Publication in this collection
    12 Feb 2021
  • Date of issue
    2021

History

  • Received
    12 Aug 2020
  • Accepted
    17 Dec 2020
  • Published
    29 Jan 2021
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