228

Journal of Vector Ecology

June 2014

Scientific Note First record of the blow fly Chrysomya megacephala (Diptera: Calliphoridae) on a southern Atlantic island: implications for disease transmission in a protected environment Rodrigo F.R. Carmo and Simao D. Vasconcelos Insects of Forensic Importance Research Group, Department of Zoology, Universidade Federal de Pernambuco, Recife – PE, 50.670-420, Brazil, [email protected] Received 24 November 2013; Accepted 1 January 2014  Flies from the family Calliphoridae comprise a cosmopolitan group of approximately 1,500 species, many of which are reported as colonizers of human and animal corpses (Carvalho and MelloPatiu 2008). Some species, such as those from the genus Chrysomya Robineau-Desvoidy, 1830, have medical relevance as vectors of pathogens, including bacteria, protozoans, and helminthes, and as causal agents of myiasis (Greenberg 1973). A study performed in Ethiopia showed that Chrysomya rufifacies acted as a vector of at least five helminthes parasites, including Ascaris lumbricoides, and four species of protozoan parasites: Entamoeba histolytica/ dispar, Entamoeba coli, Giardia lamblia, and Cryptosporidium sp. (Getachew et al. 2007). Three Chrysomya species, C. albiceps (Wiedemann 1819), C. megacephala (Fabricius 1874), and C. putoria (Wiedemann 1818), originally restricted to the Old World, were accidentally introduced in the Neotropical region in the late 1970s. Since their first detection in southern Brazil, Chrysomya species, including a fourth species, C. rufifacies, have been reported in several countries in the Americas (Mariluis and Mulieri 2003, Montoya et al. 2009, Kosmann et al. 2013). A recent review on necrophagous Diptera in northeastern Brazil indicates that Chrysomya species have spread along diverse ecosystems with varying degrees of anthropogenic impact (Vasconcelos and Araujo 2012). The current understanding of the dispersion of Chrysomya species in South America, however, is limited to mainland areas of Argentina, Brazil, Colombia, and Peru (Mariluis and Mulieri 2003, Montoya et al. 2009, Kosmann et al. 2013, Vasconcelos and Araujo 2012). So far, there are few records on the arrival and establishment of these species in insular environments despite their medical importance. As part of a study on insect ecology in the archipelago of Fernando de Noronha, a conservation site located on the coast of Brazil, we aimed to detect the presence of non-exotic, medically important Calliphoridae species. We report here the first evidence of the establishment of a nonnative Chrysomya species on islands in the southern Atlantic Ocean and discuss the implications of this finding to local disease transmission. The archipelago of Fernando de Noronha (3°52’S; 32º26’W, total area 18.4 km2), is located 545 km northeast of the Brazilian mainland. It is composed of 21 islands and islets, of which the only inhabited one, also called Fernando de Noronha, has a population of 2,630 and total area of 16.9 km2 (Brasil 2012). The archipelago is legally protected and human activities are limited or prohibited in a great portion of its territory (Freitas and Vasconcelos 2008). The climate is tropical, mean temperatures range from 23.5° C

to 31.5°C, with an annual mean of 27.0° C, relative humidity is high with an annual average of 78%, and rainfall of approximately 1,420 mm/year. Native flora are mostly represented by seasonal deciduous vegetation, with several introduced plant species. Overall, the island suffers from a persistent shortage of water, as there are no permanent freshwater reservoirs (Freitas and Vasconcelos 2008). To draw inferences regarding the relationship between the diversity of blow flies and anthropogenic activities, sampling was performed in June, 2012 in six sites to represent different levels of exposure to human activities. The sites under Low Anthropogenic Impact (LAI) included Ponta da Sapata (PS) located at the extreme west of the island, a small peninsula restricted to scientific and management activities partially covered with native vegetation and is part of the Marine National Park, and Praia de Atalaia (PA), a restricted beach located at the northeastern area of the island, open to controlled tourist visits two h per day and also part of the National Marine Park. The sites under Moderate Anthropogenic Impact (MAI) were Mangue do Sueste (MS), a mangrove area located in the southern portion of the island with limited human presence and it is an area used for egg-laying by marine turtles, Baía dos Golfinhos (BG), a bay situated in the northwest of the island, with predominantly shrubby vegetation that belongs to the Marine National Park but is open to small groups of tourists during the day. Two sites were classified as under High Anthropogenic Impact (HAI), Urban Area (UA): the village where approximately 70% of the population of the island lives, and that has litter in several areas, and Praia do Cachorro (PC), a beach near the inhabited part of the island with unlimited access and only a few bars and small amounts of litter present. Insects were collected using a suspended trap containing chicken liver or sardine (ca. 200 g, after 24 h at room temperature) as bait (Oliveira and Vasconcelos 2010). In each environment, a grid of six traps, three containing chicken liver and three containing sardine, was placed with 20 m between the traps. A total of 108 independent traps were used throughout the study. Each trap was exposed for 48 h in each environment. Adult flies collected from traps were placed in 70% alcohol until identification using the taxonomic keys of Carvalho and Mello-Patiu (2008), Carvalho and Ribeiro (2000), and Kosmann et al. (2013). Species from the Calliphoridae assemblage were classified as constant when present in >50% of the samples, accessory when collected in 25% to 50% of the samples and accidental when present in

First record of the blow fly Chrysomya megacephala (Diptera: Calliphoridae) on a southern Atlantic island: implications for disease transmission in a protected environment.

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