Check List 9(4): 763–770, 2013 © 2013 Check List and Authors Chec List ISSN 1809-127X (Available at Journal of Species Lists and Distribution

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Check List 9(4): 763–770, 2013 © 2013 Check List and Authors Chec List ISSN 1809-127X (Available at Journal of Species Lists and Distribution Check List 9(4): 763–770, 2013 © 2013 Check List and Authors Chec List ISSN 1809-127X (available at www.checklist.org.br) Journal of species lists and distribution Floristic composition of Isla de las Gaviotas, Río de la PECIES S Plata estuary, Uruguay OF Anaclara Guido 1*, Patricia Mai 1, Verónica Piñeiro 1, Dominique Mourelle 1, Mercedes Souza 1, ISTS 2 2 2,3 L Emanuel Machín , Natalia Zaldúa and Javier Lenzi 1 Universidad de la República, Facultad de Ciencias, Grupo Caubá Flora Nativa, Iguá 4225, CEP 11400, Montevideo, Uruguay. 2 Universidad de la República, Facultad de Ciencias, Asociación Averaves, Iguá 4225, CEP 11400, Montevideo, Uruguay. 3 Centro de Investigación y Conservación Marina – CICMAR. Avenida Giannattasio km 30.5, CEP 15008, Canelones, Uruguay. * Corresponding author. E-mail: [email protected] Abstract: Isla de las Gaviotas is an island located in Río de la Plata estuary, Uruguay. The aim of this study is to determine and analyze plant species composition on this island and to identify vegetation zonation patterns. An angiosperm species list was generated using a qualitative sampling technique. We registered a total of 27 species, distributed among 18 families. According to species distribution patterns on the island, we propose four vegetation zones: North, Central, Southeast Nonetheless, this site also has a remarkable number of native species, in particular Heliotropium curassavicum, which is listedand West. among Exotic Uruguayan species species comprised of conservation 52% of the concern.total number Given of that species, the loss reflecting of coastal a historyplant species of disturbance is a current in problem,the area. the proportion of native halophyte species recorded (37%) indicated the island’s importance as a relict of Uruguayan coastal vegetation. Introduction Since 1992, the protection of the island has been managed The Río de la Plata estuary possesses outstanding by a non-governmental organization (Uruguay PL 1992) biodiversity and is considered one of the world’s largest and access to the island is restricted by law (Uruguay and most dynamic aquatic systems because of its length, 3 s-1) conducted but none have been published (C. Brussa, pers. (Framiñan and Brown 1996; Vizziano et al. 2002). The comm.).PL 1992). Currently, A few surveys the island of flora is anand important fauna have nesting, been Uruguayanbreadth and coast flow extendsrate (average approximately discharge 450 is 22,000 km along m the feeding and resting area for seabirds and shorebirds Río de la Plata estuary (MTOP-UNDP-UNESCO 1979). The (Lenzi et al. unpubl. data). coastline of this estuary consists of a series of rocky points, There is a lack of baseline information regarding sandy beaches, coastal cliffs, dunes, littoral lagoons and species composition and distribution of vegetation of islands (Chebataroff 1969). In association with different coastal islands in the Río de la Plata estuary. Due to the geomorphological formations, several vegetation types are distributed, including bunchgrasses, rush vegetation and coastal grasslands (Fagúndez and Lezama 2005). Since the toimportance designing offuture Isla demanagement las Gaviotas plans. as a As refuge such, forthe flora aim late nineteenth century, the Río de la Plata coast has been ofand this fauna, study descriptive is to determine studies ofand its analyze flora may plant contribute species composition on Isla de las Gaviotas, and identify zonation patterns of the vegetation. This study will allow further highly modified by increased tourism, the introductionet alof. evaluation of the island’s current conservation status and 2011).exotic speciesThese andactivities urbanization have fragmented (Delfino and the Masciadri original contribute to the general knowledge of coastal vegetation vegetation2005; Alonso-Paz into reduced and patchesBassagoda along 2006; the coastline. Delfino in Montevideo. Within the Río de la Plata estuary there are many islands of different geological origin: some are sedimentary but Materials and Methods most are crystalline (Chebataroff 1969). The scarcity of Study site Isla de las Gaviotas (34°54’10” S, 56°06’16” W) is understanding of the diversity and distribution of their located in the Río de la Plata estuary, approximately 400 vegetationscientific studies (Vaz Ferreira on these 1950). islands Isla has de severely las Gaviotas limited is oneour m off the coast of Uruguay, opposite Montevideo (Figure of the smallest coastal islands within the estuary and has 1). The island has a total surface area of approximately been heavily disturbed by several human activities. For 17,000 m2 many years, the island has had free public access with a (estimated from Google Earth, scale 1:25000). The surface area of the, islandincluding is about the main 11,000 island m2, whichand flooded corresponds areas to the zone with vegetation cover, as the rest are largely ofhigh river flux currents, of visitors. have These probably activities, led to combined the accumulation with the rocky outcroppings. The island is of crystalline origin, ofproximity waste on of thethe island.island Asto Montevideoa result, a restoration and the influence process with a predominance of sandy substrate in the north zone was initiated, which included the elimination of rubbish and rocky outcrops in the southern zone. In the Río de la and certain pests and the planting of exotic woody species. Plata estuary, salinity varies from 1 to 32 ppt during the 763 Guido et al. | Floristic composition of Isla de las Gaviotas, Uruguay year (Fossati and Piedra-Cueva 2003). A turbidity front Species names were assigned following APG III (2009), is approximately located off the coast of Montevideo, the and nomenclature and author citations for all species were position of which varies with the combined effects of conferred in the Tropicos database (tropicos.org. Missouri several forces, such as total discharge from the Uruguay Botanical Garden 2012). Species habit (herb, tree, shrub, and Paraná Rivers into the Río de la Plata estuary, the climber) and status (native, exotic, cosmopolitan) was balance between onshore and offshore winds, and tidal assigned according to Zuloaga et al. (2008). All native et al. species were collected and deposited with a voucher 2010). number in the MVJB herbarium collection. influences (Framiñan and Brown 1996; Trimble system, the study area falls within the Cfa climate category, Results and Discussion characterizedAccording toby the a humidKöppen–Geiger subtropical climate climate classification with hot, A total of 27 species were registered on Isla de las humid summers and mild to cool winters (McKnight Gaviotas, belonging to 27 genera and 18 families (Table and Hess 2000). The mean temperature of Montevideo 1). No new species were observed in the space among is 16.5°C and total annual precipitation is 1198 mm quadrants. Most of the species were herbaceous (81.5%). (Carrasco meteorological station, DNM 2012). Amaranthaceae and Poaceae were the most species-rich families, with four species in each one. Nonetheless, most Data collection families were represented by only one species. The absence Fieldwork on Isla de las Gaviotas was carried out of Asteraceae and Cyperaceae was unexpected, given that these are very common families on the Uruguayan coast. During our surveys, we compiled a complete species list of during two field trips in November and December of 2011. These plants have various xeromorphic traits (e.g., high the main island were established at a minimum distance cellularHalophytes osmotic comprised pressure, 41% succulence, of all species leaf identified.absence, ofangiosperms. 30 m and geo-referenced Prior to fieldwork, using seven satellite sampling images points (Figure on curled leaf laminae) associated with tolerance to high 1). Sampling quadrants (30 x 30 m), centered on each salt concentrations (Chebataroff 1952; Legrand 1959). Due to the adaptive traits that permit salt tolerance or Vegetation between quadrants was also observed for the avoidance, many of these species are distributed in saline presencesampling point,of species were not used recorded to survey within floristic the composition. established environments around the world (Chebataroff 1952). The percentage of halophyte species recorded included others were determined using botanical keys and regional cosmopolitan, native and exotic species present along the quadrants. Some species were identified in the field while Uruguayan coast (Lombardo 1982; 1983; 1984). well as consultation with specialists and the herbarium Despite the important presence of native plant species, collectionflora (Legrand at the 1943; “Profesor Lombardo Atilio 1982; Lombardo” 1983; Botanical1984) as Garden and Museum (MVJB, Montevideo, Uruguay). disturbance of the site. Herbs comprised 71% (10 species) of52% exotic of species,species whilewere woodyexotic, species reflecting comprised the history 29%. of Zonation patterns Based on species composition and physiognomy of vegetation at each sampling quadrant, we proposed a zonation scheme for the entire study site. Four vegetation West (Figures 2 and 3). The North Zone was mainly characterizedzones were identified:by sandy sedimentsNorth, Central, and low Southeast plant species and cover. Among the species found exclusively in this zone, Rumex cuneifolius was the only native halophyte (Table 1; Figure 4). In addition, Atriplex prostrata was a widespread species. This species is a facultative halophyte, which exhibits its most extensive branching
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