Genotoxic and mutagenic effects of Atrazine Atanor 50 SC on Dendropsophus minutus Peters, 1872 (Anura: Hylidae) developmental larval stages.

The potential mutagenic and genotoxic effects of the herbicide atrazine were investigated in different developmental stages of Dendropsophus minutus tadpoles. These animals were exposed to 4 nominal concentrations of atrazine (2.25, 4.5, 9, and 18 mg/L) and 40 mg/L of Cyclophosphamide as a positive control, for 96 h. Negative controls were also added to the experiment. The tadpoles were divided into three groups according to Gosner's developmental stages, namely GS 25-33 as premetamorphic, GS 36-39 as prometamorphic, and GS 42-43 as metamorphic climax. Our results showed that the premetamorphic and metamorphic stages were more sensitive than the prometamorphic stage to the herbicide. A comet assay and micronucleus test for the sensitive stages demonstrated DNA damage in a concentration-dependent curve. Although a dose-response effect was not observed for the prometamorphic stage, a statistically significant difference was found between the treatment of 18 mg/L and the negative control. Moreover, the highest concentration of atrazine showed both the largest amount of DNA damage and the highest micronucleus frequency regardless of the developmental stage of D. minutus. In conclusion, atrazine was genotoxic and mutagenic for D. minutus in a dose-sensitive manner, dependent on larval developmental stages. Considering the prometamorphic stages showed no dose-response effect to atrazine, we suggest caution when using this stage in biomonitoring studies in order to avoid false negative results. Amphibians have been proven to be useful bioindicators, and we suggest replicating biomonitoring studies using different species to represent ecosystems' environmental impacts.

The advertisement and aggressive calls of Rhinella abei (Baldissera, Caramaschi, and Haddad, 2004) (Anura: Bufonidae) from Campo Largo, Paraná, Brazil.

Rhinella abei is a medium-sized species (snout-to-vent length 57.0-76.4 mm in males; 60.4-83.9 mm in females-Baldissera et al. 2004) of the Rhinella crucifer species group, distributed in the Brazilian Atlantic Rainforest, from the State of Paraná to northern Rio Grande do Sul (Frost 2016). It is recorded in forested areas (Conte & Rossa-Feres 2007), or while breeding along forest edges and open habitats. Information on advertisement calls of species in the R. crucifer group is available for R. casconi, R. crucifer, R. inopina and R. ornata (Andrade et al. 2015; Heyer et al. 1990; Oliveira et al. 2014; Roberto et al. 2014). Here we describe the advertisement and aggressive calls of R. abei recorded in the municipality of Campo Largo (25.507472° S, 49.376632° W, datum "WGS84"), southeast State of Paraná, Brazil.

Anuran Species Richness, Composition, and Breeding Habitat Preferences: a Comparison between Forest Remnants and Agricultural Landscapes in Southern Brazil.

Fabrício Hiroiuki Oda, Vinicius Guerra Batista, Priscilla Guedes Gambale, Fabio Teruo Mise, Fagner de Souza, Sybelle Bellay, Jean Carlo G. Ortega, and Ricardo Massato Takemoto (2016) The expansion of agriculture causes habitat loss and fragmentation that negatively affects biodiversity. We analyzed the species richness, composition and habitat preferences of anuran species in aquatic habitats in mesophytic semideciduous Atlantic Forest remnants and surrounding agricultural landscapes in southern Brazil, between April 2011 and March 2013. Nineteen anuran species, belonging to 11 genera and 5 families, were recorded. Species richness was similar between the forest remnants and the agricultural landscapes (18 and 19 species, respectively). Anuran species composition was associated with habitat type and the number of vegetation types in breeding habitats. Most species preferred breeding habitats in the agricultural landscape. Our results suggest that the anuran species recorded have access to both forest remnants and agricultural landscapes, as species richness in the two areas was similar. Habitat type and the number of vegetation types may influence species composition, because vegetation provides shelter and calling sites for anurans, which breed mainly in lentic water bodies. Thus, to maintain anuran populations in fragmented landscapes, it is important to preserve artificially constructed bodies of water within the agricultural landscape and on the forest edge.