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1.
Rev. bras. entomol ; 58(4): 337-342, Oct.-Dec. 2014. ilus, tab
Article in English | LILACS | ID: lil-732846

ABSTRACT

Necrophagous Diptera associated with wild animal carcasses in southern Brazil. The aim of this study was to acquire a better knowledge concerning the diversity of necrophagous Diptera that develop on wild animal carcasses. For this purpose, the decomposition of six wild animal carcasses was observed in order to collect and identify the main species of necrophagous flies associated with the decomposition process. The carcasses were found on highways near the cities of Pelotas and Capão do Leão in the initial stage of decomposition, with no significant injuries or prior larval activity. Four wild animal models were represented in this study: two specimens of Didelphis albiventris Lund, 1840; two Tupinambis merianae Linnaeus, 1758; one Nothura maculosa Temminck, 1815; and one Cerdocyon thous Linnaeus, 1766. A total of 16,242 flies from 14 species were reared in the laboratory, where Muscidae presented the greatest diversity of necrophagous species. Overall, (i) carcasses with larger biomass developed a higher abundance of flies and (ii) the necrophagous community was dominated by Calliphoridae, two patterns that were predicted from published literature; and (iii) the highest diversity was observed on the smaller carcasses exposed to the lowest temperatures, a pattern that may have been caused by the absence of the generalist predator Chrysomya albiceps (Wiedemann, 1819). (iv) An UPGMA analysis revealed a similar pattern of clusters of fly communities, where the same species were structuring the groupings.

2.
Toxicol In Vitro ; 28(3): 365-72, 2014 Apr.
Article in English | MEDLINE | ID: mdl-24325972

ABSTRACT

Sea anemones are benthic organisms, of low mobility and can be directly affected by water pollution. This work studied the defense mechanisms and DNA damage caused by copper toxicity in cells from the anemone Bunodosoma cangicum. For this, exposure of anemones cells were held, kept in primary culture through explant of podal disk to copper (7.8 and 15.6 µg/L), and the control group, for 6 and 24h. Cytotoxicity was seen through the viability and cell number, MXR phenotype through the accumulation of rhodamine-B, ROS generation by H2DCF-DA and DNA damage by comet assay. The results obtained show that there is a drop in viability and number of cells, especially after exposure of 24h in 15.6 µg/L. There is an induction of the MXR activity only at 7.8 µg/L for 24h. As for ROS, there is an increase in the generation of reactive species in greatest concentration of copper for 6h, and in both for 24h, which leads to oxidative stress, which culminates with a DNA damage. What was evidenced by the increase of the tail size, % DNA presented and moment of tail. Therefore, the copper represents an adversity to the anemones cells, being cytotoxic and genotoxic.


Subject(s)
Copper/toxicity , Oxidative Stress/drug effects , Sea Anemones/drug effects , Water Pollutants, Chemical/toxicity , Animals , Cell Survival/drug effects , Comet Assay , Copper/administration & dosage , DNA Damage/drug effects , Dose-Response Relationship, Drug , Mutagenicity Tests , Mutagens/administration & dosage , Mutagens/toxicity , Reactive Oxygen Species/metabolism , Sea Anemones/cytology , Time Factors , Water Pollutants, Chemical/administration & dosage
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