Long-term reduction of Trypanosoma cruzi infection in sylvatic mammals following deforestation and sustained vector surveillance in northwestern Argentina
Introduction
Trypanosoma cruzi, the etiologic agent of Chagas disease, has been detected in some 180 species belonging to 25 families of mammals in the Americas, with marsupials, edentates, and rodents being the most frequent sylvatic hosts (World Health Organization, 2002). Domestic transmission cycles mainly include humans, dogs and cats, and several species of triatomine bugs adapted to human dwellings (Pinto Dias, 2000). Transmission cycles of T. cruzi display large spatial and structural heterogeneity (Diotaiuti et al., 1995).
The Gran Chaco, a natural landscape unit of about 1,000,000 km2 crossing over northern Argentina, Bolivia, Paraguay and southwestern Brazil, is one of the most endemic regions for Chagas disease. Natural infection by T. cruzi has been reported for armadillos Chaetophractus vellerosus, C. villosus, Cabassous unicinctus, Dasypus novemcinctus, Euphractus sexcinctus, and Tolypeutes matacus; opossums Didelphis albiventris and Lutreolina crassicaudata; short-tailed opossums Monodelphis domestica; foxes Lycalopex culpaeus and L. gymnocercus griseus; coatis Nasua nasua, and mice Calomys musculinus and C. laucha (Carcavallo and Martínez, 1968, Yeo et al., 2005). In a well-defined area in the semiarid Argentine Chaco, the only wild mammals found infected with T. cruzi were D. albiventris opossums, a few Conepatus chinga skunks and one Galictis cuja ferret among 230 mammals from 20 species (Pietrokovsky et al., 1991, Wisnivesky-Colli et al., 1992). In the Bolivian Chaco, sylvatic Triatoma infestans, Triatoma sordida and Triatoma guasayana have been found infected with T. cruzi and may be the putative sylvatic vectors of T. cruzi (Noireau et al., 2000). In the Argentine Chaco, however, the sylvatic vector of T. cruzi has not been firmly established. Since the 1990's the Chaco has been undergoing accelerated deforestation and change of land use patterns which may have affected the relationship between the domestic and sylvatic transmission cycle of T. cruzi to an unknown extent.
T. cruzi has been classified into two major phylogenetic lineages, T. cruzi I (TCI) and T. cruzi II (TCII), and several sublineages within TCII designated as IIa, IIb, IIc, IId and IIe (Anon., 1999). These lineages appear to be distributed differentially between triatomine species and hosts throughout the Americas. TCI was originally described from sylvatic hosts and predominates in domestic transmission cycles to the north of the Amazon basin, whereas TCII predominates in domestic cycles but has sometimes been found in sylvatic mammals as well (Brisse et al., 2000, Yeo et al., 2005). In the Argentine and Paraguayan Chaco, TCI infects D. albiventris opossums and much less frequently humans and T. infestans, whereas TCII typically infects T. infestans, domestic dogs and cats, humans and skunks (Luca d’Oro et al., 1993, Diosque et al., 2003, Yeo et al., 2005, Marcet et al., 2006). Based on isoenzyme and molecular markers, two studies concluded that domestic and sylvatic transmission cycles of T. cruzi overlapped partially throughout Argentina and in two rural areas within the Chaco region (Wisnivesky-Colli et al., 1992, Luca d’Oro et al., 1993, Diosque et al., 2003). Opossums were suggested as a possible bridge between sylvatic and domestic transmission cycles (Schweigmann et al., 1999, Diosque et al., 2004). Temporal variations in the sylvatic cycle of transmission of T. cruzi in the presence of significant environmental changes have not been investigated.
As part of a longitudinal study on the eco-epidemiology of Chagas disease in a well-defined rural area in northwestern Argentina under sustained vector surveillance and selective insecticide sprays, the present study sought to assess the host range and prevalence of T. cruzi in a wide variety of wild mammals, and to identify the parasite sublineages circulating in them. Furthermore, to assess the existence of long-term variations in the dynamics and intensity of sylvatic transmission of T. cruzi, we compared our results with data collected in the same area between 1984 and 1991, before both massive deforestation around one of the villages and sustained vector surveillance in all villages was initiated in 1992.
Section snippets
Study area
Field studies were carried out in the dry forest around Amamá (27°12′30″S, 63°02′30″W) and neighboring rural villages (Trinidad, Mercedes, Pampa Pozo, Villa Matilde, San Luis and La Curva) and in an isolated settlement (Lote S), situated in Moreno Department, Province of Santiago del Estero, Argentina (Fig. 1). The area is part of the semiarid southern Chaco, with a dry season from April to October. During 2002–2004 a weather station (Weather Monitor II, Davis Co., Baltimore, MD) located in
Results
A total of 521 mammals from at least 13 identified species was captured with an overall effort of 10,718 trap-days and additional manual captures that yielded approximately half of the total catch (Table 1). Rodents (mice, moles and cavies) comprised most of the catch (n = 282) followed by skunks (n = 92), three species of armadillos (n = 90), and Didelphis opossums (n = 42). Most opossums (73%) and skunks (69%) were captured around the more forested Trinidad, Mercedes and Villa Matilde villages,
Discussion
Our study shows a dramatic decrease in the prevalence and incidence of T. cruzi infection in sylvatic hosts over nearly two decades. To our knowledge, this study may be the first to assess the existence of long-term variations in the dynamics and intensity of sylvatic transmission of T. cruzi in a well-defined area, and to provide approximate estimates of force of infection of opossums based on age-prevalence curves. Opossums were still the main sylvatic reservoir hosts of T. cruzi, followed by
Acknowledgements
We are grateful to Francisco Petrocco, Juan M. Gurevitz, Leonardo Lanati, Evelin Grijalva, M. Cruz Pino, Paula Marcet, Margarita Bisio and Rebecca Dieter for assistance in field or laboratory work. Reference strains of T. cruzi I and T. cruzi IIa, IIb, IIc, IId and IIe were kindly provided by Patricio Diosque and Miguel Angel Basombrío (Instituto de Patología Experimental, Universidad Nacional de Salta, Argentina) and by Michel Tibayrenc (UR62 “Genetics of Infectious Diseases”, IRD Centre,
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2016, Acta TropicaCitation Excerpt :Ongoing large-scale changes in land use and habitat fragmentation throughout the Gran Chaco and other affected regions may have impacted heavily on the structure and functioning of the sylvatic transmission cycles of T. cruzi. Evidence on the presumable relevance of anthropic disturbance on sylvatic transmission cycles still is sparse (Ceballos et al., 2006; Vaz et al., 2007). Dasypus novemcinctus armadillos and Didelphis opossums (including D. marsupialis, D. aurita and D. albiventris) are the most widespread sylvatic hosts of T. cruzi ; they are usually infected with T. cruzi III (TcIII) and T. cruzi I (TcI), respectively, and display large infectiousness to the vector T. infestans in the Gran Chaco and elsewhere (Alvarado-Otegui et al., 2012; Ceballos et al., 2006; Diosque et al., 2004; Orozco et al., 2013; Yeo et al., 2005).
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2015, Acta TropicaCitation Excerpt :Therefore, most of the dog infections detected before sustained interventions can be attributed to vector-borne transmission occurring in (peri)domestic habitats. Evidence of oral transmission in dogs was weak or absent during this period, but the intensity of the sympatric sylvatic transmission cycle of T. cruzi had declined substantially following increasing deforestation and habitat degradation (Cardinal et al., 2008; Ceballos et al., 2006). The frequency distribution of parasite DTUs in humans, domestic dogs and bugs differed to some extent over two decades, and the degree of overlapping between sylvatic and domestic transmission cycles apparently declined (Cardinal et al., 2008).