Temporal Variation of Population Structure of the Invasive Isognomon bicolor (Mollusca, Bivalvia), Brachidontes solisianus (Mollusca, Bivalvia) and Ulva spp. (Chlorophyta, Ulvales) Biomass, Pernambuco - Brazil  

Guimaraens M.A , Dias V.
Universidade de Pernambuco, Instituto de Ciências Biológicas, Disciplina de Biologia, Rua Arnóbio Marques, 310, 50100-130, Recife – PE, Brazil
Author    Correspondence author
International Journal of Marine Science, 2015, Vol. 5, No. 43   doi: 10.5376/ijms.2015.05.0043
Received: 01 May, 2015    Accepted: 26 Jun., 2015    Published: 07 Jul., 2015
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Guimaraens M.A and Dias V., 2015, Temporal variation of Population structure of the invasive Isognomon bicolor (Mollusca, Bivalvia), Brachidontes solisianus (Mollusca, Bivalvia) and Ulva spp. (Chlorophyta, Ulvales) Biomass, Pernambuco - Brazil, International Journal of Marine Science, 5(43): 1-5 (doi: 10.5376/ijms.2015.05.0043)


Specifically in Piedade reef, where we performed the present study, Isognomon bicolor invasive bivalve showed greater abundance in the mid intertidal band before dominated by the bivalve Brachidontes solisianus and the barnacle Tetraclita stalactifera. However, the abundance and size structure of Isognomon bicolor and Brachidontes solisianus are variable in the local collection related to desiccation and the presence of Ulva spp.. In this context, this study aims to evaluate the population structure of Isognomon bicolor and Brachidontes solisianus from density and shell length data. For that, were randomly collected 3 quadrats of 20 X 20 cm in February and May 2012, dry and rainy seasons respectively. The animals were scraped, and placed in labeled plastic bags, and frozen for later sorting. After sorting the length of the bivalve shells were measured with the aid of caliper, the seaweed Ulva spp. was also screened, dried and weighed. The Chi-Square test was used to assess the difference between the frequency distribution of the different size classes. The bivalves were divided into 10 size classes. The chi-square test detected a significant difference between the population structure of bivalves. Isognomon bicolor had lower density in May 2012 during the drought, while more individuals Brachidontes solisianus were found in May. However the largest proportion of individuals was always between 13-16 mm in both months of collection for Isognomon bicolor and 3 mm for Brachidontes solisianus presenting both bivalve unimodal distribution these sizes could be more resistant to desiccation and predation stress. The Mann-Whitney test showed a lower density for Ulva spp. in May 2012.

Sandstone reefs; Shellfish bioinvasion; Macroalgae; Isognomon bicolor; Brachidontes solisianus; Brazilian coast

1 Background
The coastal region of Pernambuco state is approximately 187 km in length and has the characteristic sandstone reefs that are marine outcrops that form parallel strands along the coast. These reefs are the result of consolidation or lithification of beach sand by calcareous or ferruginous cementing, and are made especially from quartz and bioclasts, mainly molluscs and algae (Sousa & Cocentino, 2004). Many of these environments are the main substratum for attachment of algae and benthic invertebrates in intertidal areas and on the coast below, therefore being an ecosystem with biological interactions that have significant importance in the structure of populations (Almeida et al., 2008, Guimaraens et al., 2011). Bivalve molluscs of the genus Brachidontes live in the intertidal zone of coves and bays and fix byssus to substrate rocky and reef surfaces, forming clusters of hundreds of individuals.
Numerous exotic species carried in ballast water and hull vessels have been introduced in the Brazilian coastal ecosystems (Farrapeira et al., 2011), so it is important to know aspects of the biology of these exotic species in the new environment and the potential impact on species previously established, for conservation and management of marine ecosystems invaded since invasive species can reduce biodiversity. The Isognomon bicolor (C.B. Adams, 1845) invasive bivalve colonization in the Brazilian coast has been from the State of Rio Grande do Norte to Santa Catarina (Domaneschi & Martins, 2002; Breves-Ramos et al., 2010; Zamprogno et al., 2010;. Martinez, 2012), having already been cited for the Pernambuco coast (Silva & Barros, 2011). Whereas Brachidontes solisianus (Orbigny, 1846) is distributed on the Atlantic Coast from Mexico to Uruguay (Rios, 1994).

Mussels in intertidal communities are dominant organisms on rocky shores and reefs because they are frequently superior competitors for space in these communities (Barbiero et al., 2011). Studies have shown that mussels can add complexity to benthic communities and increase species richness and diversity in the intertidal zone. Brachidontes solisianus is a small bivalve belonging to Mytilidae family. The free swimming larva of this species recruits on shallow and hard substrate and algae bases bound by byssus (Monteiro-Ribas et al., 2006). These aggregates can reduce mortality from desiccation and temperature stress. Isognomon bicolor have been found fixed by their byssus on rocky coasts and occurring together with Ulva spp. (Fernandes et al., 2004).

Given the potential risks of bioinvasion along with knowledge on the biological diversity of this area, it is necessary to study the characteristics of the animal communities that inhabit the beach of Piedade, not only to evaluate possible damage, but also to the knowledge of current biodiversity. It is extremely important to study the environment containing subsidies for the installation of invasive species. In addition to preparing a floristic survey to check the health of the reef and the interaction with individuals who also live on site during periods of dry and rainy seasons.

The objective of the study was to evaluate the population structure of Isognomon bicolor and Brachidontes solisianus in the dry and wet seasons in Piedade Beach reef  and assess the biomass Ulva spp. (Delile, 1813) on the same site and collection periods which is related to the bivalves populations recruitment and occurrence.

2 Results
In February 2012, the water temperature was 28. 3℃ and salinity of 34, while the temperature in May was 27.6℃ and salinity was 38 at Piedade Beach (Figure 1). Rainfall of the month before the first collection was 198.6 mm, and from the month before the second collection was 55.8 mm, featuring a dry period that ran during the rainy season.


Figure 1 – Sampling Site


The Chi-Square test detected a significant difference between the population structure of bivalve Brachidontes solisianus (p < 0.01) for the months of February and May. Brachidontes solisianus showed higher density of individuals in the smallest size class less than 1 mm in February 2012 (218 individuals /m2) than in May 42 individuals / m2 (Table 1). Whereas 3 mm size class that was the one with the highest density in both seasons, being higher in May 2012 (1046 individuals /m2). The dominant algae in terms of biomass was Ulva spp., also characteristic of this patch of reef.


Table 1 – Size Classes abundance and Percentage for Brachidontes solisianus at Piedade Beach in 1 m2


Ulva spp. biomass was lower in May during the drought (11.92 g dry weight /m2), showing the harmful effect of desiccation on this abundant algae in the upper mesolittoral in February (107.75 grams of dry weight /m2, p <0.05). This alga has been correlated with the recruitment of Brachidontes solisianus in the area (Guimaraens et al., 2013) since May and June have been a recruitment months and in the present study we found February as a recruitment month (Figure 2). Probably related to the abundance of Ulva spp. and less desiccation stress which can affect the abundance of Isognomon bicolor as well (Figure 3). The effect of drought was also showed by the lack of brown algae Dictyota and Dictyopteris in May 2012 (Simões et al., 2009, Table 2).


Figure 2 – Distribution by size class of Brachidontes solisianus the size classes are less than 1 mm (1) to 1 up to 8 mm (9) and 11 mm represented by 10 in the month of May (B) in 1200 cm




Figure 3 – Distribution by size class of Isognomon bicolor with classes from 1 to 4 (1) up to 37 to 40 (10) in 1200 cm2 in February (A) and May (B) 




Table 2 – Flora from the quadrats collected at Piedade Beach 


We recorded a fauna and flora, as bivalve companion, with the presence of Tetraclita stalactifera (Lamarck, 1818) barnacles and Chthamalus bisinuatus (Pilsbry, 1916) also abundant in mesolittoral zone where the bivalves were collected. Brachidontes solisianus had its highest density in both months in the 3 mm size class and yet rated as juvenile probably a size that resists more desiccation and predation as well. The Chi-Square test also showed a difference between size classes distribution for Isognomon bicolor (p<0.05). The highest percentage was 26.78% in 13 – 16 size class for Isognomon bicolor in May with the next percentage in February for the same class (26%) which showed some similarity in the distribution of size classes (Table 3). However, numerically the largest Isognomon bicolor density was in February. As for Brachidontes solisianus, the highest percentage was in February 25.93 to 3 mm size range showing an increase in their density from February (979 individuals / m2) to May (1046 individuals / m2).


Table 3 – Size Classes abundance and Percentage for Isognomon bicolor at Piedade Beach in 1 m2


3 Discussion
The higher density of Brachidontes solisianus in May could represent the growth of the animals given that the most common form of ecological succession observed in Piedade was the closing side of the Brachidontes solisianus patch (Guimaraens et al., 2013). The drying can damage the colonization of Isognomon bicolor and Brachidontes solsianus given the positive relationship of these animals with the presence of algae such as Ulva, Sargassum and calcareous articulated algae (Fernandes et al., 2004, López & Coutinho, 2010a, Martinez, 2012, Guimaraens et al., 2013).

Individuals of Isognomon bicolor are aggregated into crevices with higher densities in these places, which was also observed in Piedade Reef. Isognomon bicolor was observed colonizing empty shells of Tetraclita stalactifera (Zamprogno et al., 2010), as well as Brachidontes solisianus (Guimaraens et al., 2013), which discloses a way to reduce drying. Considering that Brachidontes solisianus had higher density in the period of drought (May 2012), despite the higher number of Isognomon bicolor in both collections, the results suggest that Isognomon bicolor and Brachidontes solisianus can interact and coexist although Isognomon bicolor has become dominant where previously the dominance was from barnacles and mussels.

The invasive Isognomon bicolor occupies the area previously dominated by barnacles such as Tetraclita stalactifera and the bivalve Brachidontes solisianus since it has a larger size than Brachidontes and has the habit of growing over each other, which can optimize space for growth. These invasive bivalves, are less preferred by local predators, such as Stramonita haemastoma Linnaeus, 1767, than native species (López et al., 2010b). Despite the higher number of Isognomon bicolor, Brachidontes solisianus had its highest density in the month of May corresponding to a period of drought during the rainy season, but Brachidontes solisianus had fewer recruits in May 2012 possibly correlated with the decrease in biomass of Ulva spp.. The bivalves showed unimodal distribution with the same class most abundant size in two collections showing some stability despite the environmental impacts such as trampling and desiccation.

4 Materials and Methods
To assess the density of invertebrates and Ulva spp. biomass were randomly collected three quadrats of 20 x 20 cm on February 6 and May 5, 2012, in dry and wet seasons, respectively in the intertidal region of the southern end of Piedade Reef 08º09'17 "- 08º13'29" S. In the top midlittoral where both Brachidontes solisianus and Isognomon bicolor co-occur. The water temperature and salinity were measured with the aid of a digital thermometer and a refractometer. Rainfall data were obtained from the INMET website (http://www. inmet.gov.br/). The organisms were scraped and placed and labeled plastic bags and frozen for screening. After the sorting with the aid of a sieve of 300 micrometers the bivalves shell length were measured with a caliper. Aluminum baskets were previously weighed, where the algae were placed and taken to oven at 60 degrees Celsius for 24 hours. The baskets were weighed again in analytical scale to access the dry weight of algae, taking the values of those empty baskets from the dried seaweed. The Mann-Whitney test was done to evaluate the difference of Ulva between collection dates (February and May). The Chi-Square test was used to assess the difference between the frequency distribution of the size classes in the different sampled seasons. The statistical analyses were made with the software Biostat.

Author's Contributions
MAG and VD conducted the field work VD sorted and measured the bivalves and MAG analyzed the data.


Almeida L.R., Guimaraens M.A., Luz B.R.L., and Porto-Neto F.F., 2008, Interação entre processos de colonização e sucessão ecológica de comunidades bioincrustantes na Praia de Piedade, Tropical Oceanography, 36: 40-46

Barbiero D. C., Macedo B. P., Masi B. P., and Zalmon I. R., 2011, A removal disturbance effect on the ecological succession of a benthic intertidal community-south-eastern Brazil, Marine Biodiversity Records, 4: 1-8

Breves-Ramos A., Junqueira A.R.O., Lavrado H.P., Silva S.H.G., and Ferreira- Silva M.A.G., 2010, Population structure of the invasive bivalve Isognomon bicolor on rocky shores of Rio de Janeiro State (Brazil), Journal of Marine Biology Association UK, 90: 453-459

Domaneschi O., and Martins C.M., 2002, Isognomon bicolor (C.B. Adams) (Bivalvia,Isognomonidae): primeiro registro para o Brasil, redescrição da espécie e considerações sobre a ocorrência e distribuição de Isognomon na costa brasileira, Revista Brasileira de Zoologia, 19: 611-627

Farrapeira C.M.R., Tenório D.O., and Amaral F.D., 2011, Vessel biofouling as an inadvertent vector of benthic invertebrates occuring in Brazil, Marine Pollution Bulletin, 62: 832-839

Fernandes F.C., Rapagnã, L.C., and Bueno, G.B.D., 2004, Estudo da população do bivalve exótico Isognomon bicolor (C.B. Adams, 1845) (Bivalvia, Isonomonidae) na Ponta da Fortaleza em Arraial do Cabo – RJ, In: Silva, J.S.V., and Souza, R.C.C.L. (eds.), Água de Lastro e Bioinvasão, Editora Interciência, Rio de Janeiro, Brazil, pp. 132-141.

Guimaraens M.A., Luz B. R. A., Silva J.F., and Carneiro J.P.S., 2011 Modeling the succession of barnacles and mussels on a sandstone reef in Pernambuco State, Brazil Hydrobiologia, 658: 365-372

Guimaraens M.A., Carneiro J. P. S., Luz B.R.A. and Silva J.F., 2013, Brachidontes solisianus (Bivalvia: Mytilidae) re-colonization dynamics on a sandstone reef at Pernambuco – Brazil. In: Nowak J., and  Kozlowski M. (eds.), Mussels ecology, life habitats and control, Nova Science Publishers, New York, USA, pp. 137-148

López M.S., and Coutinho R., 2010a, Positive interaction between the native macroalgae Sargassum sp. and the exotic bivalve Isognomon bicolor? Brazilian Journal of  Oceanography, 58: 69-72

López M.S., Coutinho R., Ferreira C.E.L., and Rilov G., 2010b, Predator-prey interactions in a bioinvasion scenario: differential predation by native predators on two exotic rocky intertidal bivalves, Marine Ecology Progress Series, 403: 101-112

Monteiro-Ribas W., Rocha-Miranda F., Romano R.C., and Quintanilha J., 2006, Larval development of Brachidontes solisianus (Bivalvia, Mytilidae), with notes on differences between its hinge system and those of the mollusk Perna perna, Brazilian Journal of Biology, 66: 109-116

Martinez A.S., 2012, Spatial distribution of the invasive bivalve Isognomon bicolor on rocky shores of Arvoredo Island (Santa Catarina, Brazil), Journal of  Marine Biology Association of UK, 92: 495–503

Silva E.C., and Barros F., 2011, Macrofauna bentônica introduzida no Brasil: Lista de espécies marinhas e ducículas e distribuição atual. Oecologia Australis, 15:326-344

Simões, I.P., Guimaraens M.A., Oliveira-Carvalho M.F., Valdevino J., and Pereira S.M.B., 2009, Avaliação florística e sucessão ecológica das macroalgas em recifes na praia de Piedade – PE, Neotropical Biology and Conservation, 4: 49-56

Souza, G.S., and Cocentino A L.M., 2004,  Macroalgas como indicadora da qualidade ambiental, Tropical Oceanography, 32: 1-22

Rios E C., 1994, Seashells of Brazil. Rio Grande, Brazil, Museu Oceanográfico da Furg, pp. 368

Zamprogno G.C., Fernandes L.L., and Fernandes F.C., 2010, Spatial variability in the population of Isognomon bicolor (C.B. Adams, 1845) (Mollusca, Bivalvia) on rocky shores in Espírito Santo, Brazilian Journal of Oceanography, 58: 23-29

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