SciELO - Scientific Electronic Library Online

 
vol.40 número1Etmopterus brachyurus Smith & Radcliffe, 1912 (Chondrichthyes, Dalatiidae): primer registro en aguas del Pacífico orientalExamen rápido de microorganismos en aguas de lastre índice de autoresíndice de assuntospesquisa de artigos
Home Pagelista alfabética de periódicos  

Serviços Personalizados

Journal

Artigo

Indicadores

Links relacionados

Compartilhar


Revista de biología marina y oceanografía

versão On-line ISSN 0718-1957

Rev. biol. mar. oceanogr. v.40 n.1 Valparaíso jul. 2005

http://dx.doi.org/10.4067/S0718-19572005000100009 

 

Revista de Biología Marina y Oceanografía 40(1): 71 – 75, julio de 2005

NOTAS CIENTIFICAS

First record of Parandalia tricuspis (Müller, 1858) and Sigambra cf. tentaculata (Treadwell, 1941) (Pilargidae: Polychaeta) in Argentina

Primer registro de Parandalia tricuspis (Müller, 1858) y Sigambra cf. tentaculata (Treadwell, 1941) (Pilargidae: Polychaeta) en Argentina

 

Julieta R. Palacios1, Claudia S. Bremec2, M. Silvia Rivero1 and Rodolfo Elías1

1Departamento de Ciencias Marinas, Universidad Nacional de Mar del Plata.
 Deán Funes 3350. B 7602 AYL. Mar del Plata, Argentina

2Instituto Nacional de Investigación y Desarrollo Pesquero (INIDEP) – CONICET.
 Paseo Victoria Ocampo nº 1, CC 175. B 7602 HSA. Mar del Plata, Argentina
 roelías@mdp.edu.ar


RESUMEN

Parandalia tricuspis (Müller 1858) y Sigambra cf. tentaculata (Treadwell 1941) fueron registrados en áreas submareales frente a Mar del Plata (38°S, 57°W, Argentina). Ésta constituye la primera mención de P. tricuspis en aguas argentinas. El género Sigambra era conocido para la región patagónica; la presente cita extiende hacia el norte su distribución. El tipo sedimentario (arenas finas y muy finas) y el contenido orgánico parecen ser los factores determinantes para el asentamiento de P. tricuspis, cuyos ejemplares fueron recolectadados tanto en aguas abiertas como dentro del puerto de la ciudad. Sigambra cf. tentaculata solo fue recolectada en el puerto, en sedimentos fango arenosos con alto contenido de materia orgánica.

Key words: Pilargids, subtidal, port, sediment type, benthos


INTRODUCTION

Polychaetes of the family Pilargidae are a group of euribathic organisms and, according to Hartman (1947), with wide distribution. They live in soft-bottom substrates, although with no dominance in terms of abundance or richness (Salazar-Vallejo 1986). Pilargids are not tube builders, and due to their anatomical structure (sack-like pharinx) they are considered carnivores or omnivores (Fauchald & Jumars 1979). Systematics of pilargids was confuse and several species have been changed from one genus to another. The family has been revised by Hartman (1947), Pettibone (1966), Emerson & Fauchald (1971) and Salazar-Vallejo (1986).

Previous records of pilargids in South America were made along the coast of Chile (Wesenberg-Lund 1962, Hartmann-Schröder 1965, Hartmann 1967, Cañete et al. 1990, Rozbaczylo & Quiroga 2000) and southern Brazil (Nonato 1981, Lana 1984, Salazar-Vallejo 1990). Records in argentinean waters are scarce. Ancistrosyllis groenlandica McIntosh 1879 was registered for Drake Channel and Malvinas (Falkland) Islands by Hartman (1947), and posteriorly Salazar-Vallejo & Orensanz (1991) extended its distribution to Uruguay and
Argentina. These authors also identified fragments of Pilargis cf. maculata Hartman 1947 from subtidal beds of Mytilus at 38°S, in argentinean waters, and Parandalia tricuspis and Sigambra tentaculata only in uruguayan localities (Salazar-Vallejo & Orensanz 1991, J.M. Orensanz pers. comm. 2003).

In a general survey of the subtidal macrobenthos off Mar del Plata, pilargids were collected at two different sites: shallow waters close to the intertidal sewage discharge and the city harbor. The organisms were identified as Parandalia tricuspis (Müller 1858) and Sigambra cf. tentaculata (Treadwell 1941). Both constitute new records for argentinean waters. The present work shows ecological aspects of these species, like relationships of abundance and size of specimens according to the type and contents of organic matter in the bottom, and removal of sediments due to storms.

MATERIAL AND METHODS

The material examined was taken from shallow bottoms between 4-14 m depth and 200 m - 5 km offshore, from the sewage discharge. Quantitative samplings were carried out from December 1999 to March 2002. Samples were collected before and after a storm event during March 2002. An additional survey was carried out in Mar del Plata harbor in December 2001 (Fig. 1).

 

Figure 1. Sampling areas around Mar del Plata city. Pilargids were found in two sites:
off the sewage discharge, and the harbor city

Figura 1. Áreas de muestreo alrededor de la ciudad de Mar del Plata. Los pilárgidos fueron hallados en dos sitios:
frente a la descarga cloacal, y en el puerto

Sampling was done with a van Veen type grab of 0.05 m2. Three to four grabs were taken for biological analysis, and one or two extra grabs for sedimentological analysis. Total organic carbon was determined according to Walkley & Black (1965).

Median density was estimated; individual size was measured in complete specimens for testing (t-student) differences between pre- and post-storm samples and between harbor and offshore samples.

RESULTS AND DISCUSSION

Parandalia tricuspis (Müller 1858)

Material examined

The total number of specimens collected was 492, 12 from the city harbor (32.73-71.05 mm in length) and the rest from the area influenced by the sewage discharge (1.55-23.24 mm in length) (Table 1).

Table 1. Sampling stations and number of specimens of Parandalia tricuspis collected at the study area
Tabla 1
. Estaciones de muestreo y número de especimenes de Parandalia tricuspis en el área de estudio

Parandalia tricuspis was identified following Salazar-Vallejo & Orensanz (1991). The material fits well with the redescription published by Salazar-Vallejo (1990), except for the number of neurosetae in each fasciculum, 12 in uruguayan individuals and 4 in our material from Argentina. However, the number of neurosetae in posterior fascicles is not considered a diagnostic character to the specific level (Parker 1996)1.

Habitat

Parandalia tricuspis was found in fine to very fine sandy sediments in the zone of sewage discharge, with a mean organic carbon content of 0.54%. The species was absent in coarser surrounding bottoms with lower organic carbon content of 0.28%. Density was 400 and 2,500 ind.m-2 in December and March, before and after the storm, respectively (Fig. 2). The sediment type was muddy-sandy, with mean organic carbon content of 1.83% at the harbor, where density was 38 ind.m-2 (Fig. 2). Mean individual size was lower after the storm (4.44 mm), while before the storm and at the harbor, organisms were larger (5.48 and 33.5 mm, respectively). These differences were highly significant (P<0.01).

Figure 2. Median density of Parandalia tricuspis at the Mar del Plata area. Sampling in the harbor was performed during December 2001. In March 2002 sampling was carried out before (be-s) and after (af-s) a storm
Figura 2. Densidad mediana de Parandalia tricuspis en el área de Mar del Plata. El muestreo en el puerto fue realizado en diciembre de 2001. En marzo de 2002 el muestreo se realizó antes (be-s) y después (af-s) de una tormenta

Remarks

These results suggest that sediment type is a limiting factor in the distribution of this species, only collected in finer bottoms of the area. For pilargids, a positive relationship to fine sand was found, although in general terms, polychaetes are related to a combination of sediment, organic content and depth (Méndez & Green-Ruiz 1998). Specimens of P. tricuspis were larger at the harbor area than in pre-storm shallow samples, although the presence of small-sized organisms was related to contaminated environments (see Pearson & Rosenberg 1978). Bottoms deeper than 6 m off the domestic sewage discharge are not contaminated by organic pollution (Elías et al. 2001, 2004). In the subtidal areas off Mar del Plata, local hydrodynamics and periodical storm disturbance are the main factors structuring benthic assemblages, producing cyclical changes and forcing communities to restart sucession (Palacios et al. 20012, Elías et al. 2004, Elías et al. in press). This fact agrees with the observed pattern in mean size of this pilargid species before and after the storm.

Sigambra cf. tentaculata (Treadwell 1941)

Material examined

Station 6 (38º02.54’S-57º31.83W; 4 complete specimens; 10,4 m; anoxic mud), station 4 (38º02.37’S-57º32.02’W; 2 complete specimens; 9 m; muddy). The mean size of specimens was 12.52 mm length, ranging from 5.42 to 30.98 mm.

The studied material fits well with the redescriptions given by Salazar-Vallejo & Orensanz (1991) and Leon-Gonzalez (1991). Moreira & Parapar (2002) redescribed S. tentaculata (Treadwell 1941) from type-material and re-established S. parva (Day 1963), previously considered synonyms, based on differences in the arrangement and number of papillae on the proboscis. We could not observe these characters in our stained (Rose of Bengal) specimens, so we decided to refer this specimens as S. cf. tentaculata.

Habitat

The specimens were found in only 2 of the 11 stations analyzed, in muddy-sandy bottoms with high organic matter contents between 2.14 and 1.06 %, with densities of 76 and 19 ind.m-2, respectively. The two stations were placed between the mouth and the inner region of the harbor, where bottoms are stable and not affected by contamination or hydrodinamism (Rivero et al. 2003)3.

The genus Sigambra was previously cited in very fine to fine sandy beaches at Puerto Madryn (43°S, 65°W) (Escofet 1983) and according to J.M. Orensanz (pers. comm.) the material also corresponds to Sigambra cf. tentaculata.

ACKNOWLEDGEMENTS

To the Soil Laboratory of Instituto Nacional de Tecnología Agropecuaria (INTA – Balcarce) for organic carbon determination. Water column measurements were performed by personnel of the enterprise Obras Sanitarias Sociedad de Estado (OSSE). We are indebted to Dr. Paulo da Cunha Lana (UFPR – Brazil), Dr. K. Fauchald (NMNH – U.S.A), Dr. J.M. ‘Lobo’ Orensanz (CenPat – Argentina) and Dr. N. Rozbaczylo (PUCC – Chile) for bibliography and advice. Samplings were taken from the “ARA Luisito”, Escuela Nacional de Pesca. This work was read in the VIII International Polychaete Conference. Madrid (Spain), 5-9 July, 2004. This is Department of Ciencias Marinas (UNMdP) contribution N° 116 and INIDEPcontribution N° 1358.

NOTES

1. Parker T. [mblcsdla@netcom.com] “Misdiagnosis of Parandalia ocularis (Polychaeta: Pilargidae).”     http://www.keil.ukans.edu/~worms/parandal.html October 1996.

2. Palacios JR, EA Vallarino, MS Campodonico & R Elias. 2001. Resiliencia en comunidades macrobentónicas submareales del Atlántico SO: vertidos cloacales y tormentas como fuerzas estructurantes en el corto plazo. Extended Abstracts of IX COLACMAR, San Andrés, Colombia.

3. Rivero MS, R Elías & EV Vallarino, 2004. Polychaetes as indicators of environmental health in the Mar del Plata harbor, Argentine. 8th International Polychaete Conference, Madrid, July 4-8, 2004.

 

LITERATURE CITED

Cañete JI, VA Gallardo & FD Carrasco. 1990. On the presence of Pilargis berkeleyae Monro, 1933 (Polychaeta, Pilargidae) in the soft-bottoms of central Chile shelf. Boletin de la Sociedad de Biología de Concepción (Chile) 61: 153-156.        [ Links ]

Elías R, CS Bremec & EA Vallarino. 2001. Polychaetes from a southern shallow shelf Atlantic area (Argentina, 38º S) affected by sewage discharge. Revista Chilena de Historia Natural 74: 523-531.        [ Links ]

Elías R, EA Vallarino, M Scagliola & FI Isla. 2004. Macrobenthic distribution pattern at a sewage disposal site in the inner shelf off Mar del Plata (SW Atlantic). Journal of Coastal Research 20 (3): 1176-1182.        [ Links ]

Elías R, JR Palacios, MS Rivero & EA Vallarino. In press. The short-term response of subtidal sand-bottom macrozoobenthic assemblages to the sewage discharge and storm effects off Mar del Plata city, Argentina (SW Atlantic). Journal of Sea Research.        [ Links ]

Emerson RR & K Fauchald. 1971. A revision of the genus Loandalia Monro with description of a new genus and species of Pilargid Polychaete. Bulletin Southern California Academy of Sciences 70: 18-22.        [ Links ]

Escofet A. 1983. Community ecology of a sandy beach from Patagonia (Argentina, South America). Master of Science Thesis, University of Washington, 122 pp.        [ Links ]

Fauchald K & PA Jumars. 1979. The diet of worms: a study of Polychaete feeding guilds. Oceanography and Marine Biology Annual Review 17: 193-284.        [ Links ]

Hartman O. 1947. Polychaetous Annelids. Part VIII. Pilargidae. Hallan Hancock Pacific Expedition 10: 483-523.        [ Links ]

Hartman O. 1967. Polychaetous annelids collected by the USNS Eltanin and Staten Island Cruises, chiefly from Antarctic Seas. Allan Hancock Monographs in Marine Biology 2: 1-387.        [ Links ]

Hartmann-Schröder G. 1965. Zur Kenntnis des sublitorals der chilenischen Küste unter besonderer Berücksichtigung der Polychaeten und Ostracoden. T1. II. Die Polychaeten des Sublitorlas. Mitteilungen aus dem Hamburguischen Zoologischen Museum und Institut 62 (spl.): 59-305.        [ Links ]

Lana PC. 1984. Anelídeos poliquetas errantes do litoral do Estado do Paraná. Tese de Doutorado. Instituto Oceanográfico, Universidade de São Paulo, 275pp.        [ Links ]

León-Gonzalez JADe. 1991. Poliquetos de fondos blandos de la costa occidental de Baja California Sur, México. I. Pilargidae. Cahiers de Biologie Marine 32: 311-321.        [ Links ]

Méndez N & M Green Ruiz. 1998. Superficial sediments and their relation to polychaete families in a subtropical embayment, Mexico. Revista de Biología Tropical 46 (2): 55-66.        [ Links ]

Moreira J & J Parapar. 2002. Redescription of Sigambra tentaculata and re-establishment of S. parva (Polychaeta, Pilargidae) based upon type material. Cahiers de Biologie Marine 43: 99-109.        [ Links ]

Nonato EF. 1981. Contribuição ao conhecimento dos anelídeos poliquetas bentônicos da plataforma continental brasileira, entre Cabo Frio e o Arroio Chuí. Tese de Livre Docência. Instituto Oceanográfico. Universidade de São Paulo, 248 pp.        [ Links ]

Pearson TH & R Rosenberg. 1978. Macrobenthic succession in relation to organic enrichment and pollution of the marine environment. Oceanography and Marine Biology Annual Review 16: 229-311.        [ Links ]

Pettibone MH. 1966. Revision of the Pilargidae (Annelida: Polychaeta), including descriptions of new species, and redescription of the pelagic Podarmus ploa Chamberlin (Polynoidae). Proceedings of the United States National Museum 118: 155-207.        [ Links ]

Rozbaczylo N & E Quiroga. 2000. Family Pilargidae (Polychaeta): new distributional ranges and a new record for the Chilean coast. Revista Chilena de Historia Natural 73: 643-651.        [ Links ]

Salazar-Vallejo SI. 1986. Pilargidae (Annelida: Polychaeta) de México: lista de especies, nueva especie y biogeografía. Cahiers de Biologie Marine 27: 193-209.        [ Links ]

Salazar-Vallejo SI. 1990. Redescription of Sigambra grubii Müller, 1858 and Hermundura tricuspis Müller, 1858 from Brazil and designation of neotypes (Polychaeta: Pilargidae). Journal of Natural History 24: 507-517.        [ Links ]

Salazar-Vallejo SI & JM Orensanz. 1991. Pilárgidos (Annelida: Polychaeta) de Uruguay y Argentina. Cahiers de Biologie Marine 32: 267-279.        [ Links ]

Walkley A & CA Blake. 1965. Organic carbon. Chapter 4. In: Black CA (ed), Method of soil analysis. American Society of Agronomy, pp. 1372-1375.        [ Links ]

Wesenberg-Lund E. 1962. Reports of the Lund University Chile Expedition 1948-49, 43: Polycheta Errantia. Lunds Univeritets Årsskrift, new series, section 2 57: 1-137.        [ Links ]

Recibido en agosto de 2004 y aceptado en enero de 2005

 

 

Creative Commons License Todo o conteúdo deste periódico, exceto onde está identificado, está licenciado sob uma Licença Creative Commons