versão impressa ISSN 1415-790X
Rev. bras. epidemiol. vol.15 no.3 São Paulo Set. 2012
Rubens Antonio da Silva; Vanessa Taís Cruz Mercado; Lúcia de Fátima Henriques; Ricardo Mário de Carvalho Ciaravolo; Dalva Marli Valério Wanderley
Departamento de Combate a Vetores - Superintendência de Controle de Endemias - Secretaria de Estado da Saúde de São Paulo
The aim of this study was to analyze the magnitude and trend of American Tegumentary Leishmaniasis (ATL) in the State of São Paulo from 1975 to 2008. An ecological study that classified municipalities according to the magnitude of transmission was performed. From 1975 to 1985, 1,281 cases of ATL were registered in 45 municipalities, rising to 258 municipalities and 4,093 cases from 1986 to 1995; and reaching 385 municipalities and 7,604 cases from 1996 to 2008. Lutzomyia intermedia s.l. was collected in most of the entomological surveys. In the classification of municipalities according to magnitude, 67.5% were observed to have a "small magnitude," 19.2% "moderate magnitude" and 13.3% "high magnitude." The highest incidences of ATL have been restricted to underserved areas close to the Atlantic fo-rest. There was an increase in the number of municipalities with small occurrence of cases and expansion in the area of risk.
Keywords: American Tegumentary Leishmaniasis. Entomological Surveillance. Control. Epidemiology. State of Sao Paulo. Brazil.
The American Tegumentary Leishmaniasis (ATL) is a zoonosis widely spread around the American continent, extending from the Southern United States to northern Argentina. It is considered to be one of the most relevant infectious diseases in this continent1. In the last 20 years, in Brazil, the number of ATL cases and its geographic occurrence have increased. Currently, this disease is found in all Brazilian states, with different epidemiological profiles and transmission patterns2.
In the state of São Paulo, ATL is an endemic disease transmitted by insects of the Order Diptera, Family Psychodidae, mostly belonging to the genus Lutzomyia and having two epidemiological patterns of transmission: the first one involves human beings coming into contact with the wild enzootic cycle; and the second one involves household transmission and human beings, synanthropic animals and Phlebotominae species that are adapting to rural and peri-urban environments3, in areas where the natural environment has greatly changed. Currently, the ATL transmission in the state of São Paulo is considered to remain associated with the place where the case has been recorded and the woods; this disease has affected all age groups regardless of gender. In the past, ATL had a localized geographical aspect and high incidence in workers who performed forest-related activities4. This situation changed with the years and a new epidemiological profile appeared in the 1970s, in which the occurrence of sporadic and/or small outbreaks characterizes the current pattern of ATL transmission in the state of São Paulo5 6 7.
The steady increase in the number of cases led to the formation of an inter-institutional group in 1993, under the coordination of the Centro de Vigilância Epidemiológica da Secretaria de Estado da Saúde de São Paulo (CVE/SES/SP - State of São Paulo Department of Health Epidemiological Surveillance Center) and participation of the Superintendência de Controle de Endemias (SUCEN - Center for Endemic Disease Control) and Instituto Adolfo Lutz (IAL - Adolfo Lutz Institute) to reassess the Technical Norms of American Tegumentary Leishmaniasis Epidemiological Surveillance and Control. In this group, SUCEN was responsible for the assessment and development of an information system for entomological surveillance, case reporting and feedback of information to Health Services9. The Surveillance System is defined as a passive system, where reports derived from the public health network through primary health centers (PHC) are mandatory when a case is confirmed. Nonetheless, although efforts have been made for prompt reporting, the underreporting of an important number of cases is still observed9.
With regard to entomological surveillance, Lutzomyia intermedia s.l. (Lutz & Neiva, 1912) has been pointed out as the most important taxon in the current epidemiological profile of ATL in the state of São Paulo, due to its predominance in altered environments and constant presence in the intra and peridomicile7 10 11 12 13, although being considered as a well-defined species complex: Lu. intermedia s.str. and Lutzomyia neivai14 15. However, transmission cannot be only attributed to Lu. intermedia s.str. 10 16. This taxon has a major role as a vector of Leishmania (Viannia) braziliensis in the home environment, whereas Lutzomyia whitmani (Antunes & Coutinho, 1939) and Lutzomyia migonei (France, 1920) have this role in the out-of-home environment17.
The present study aimed to analyze the magnitude and trend of ATL in the cities of the state of São Paulo, between 1975 and 2008, with the purpose of supporting the control program developed by the state.
An ecological descriptive study was conducted to analyze secondary data on autochthonous ATL cases and their geographical distribution, obtained from the CVE/SES/SP between 1975 and 2008; and information about the entomological surveys conducted by SUCEN and originated from the confirmation of autochthonous cases between 1985 and 2008.
The entomological survey methodologies used were as follows: without luminous bait, in a resting place, in the intradomicile or on the walls of outbuildings, with a minimum duration of three hours, using Castro traps, a deadly chamber or manual aspirator on the inner walls of the home with the use of the sheet technique when these walls are not dark or plastered; with luminous bait, using CDC electric traps installed in different points of the possible place of transmission in the home, from dusk to dawn, with a duration of 12 hours; and Shannon trap for three hours after dusk, preferably situated in the peridomicile or by the edge of the woods when these are close to the home8. The objective of the entomological traps is to identify the vector species instead of quantifying it. Species were classified according to the classification developed by Young & Duncan, 199418.
In the present study, the Lu. intermedia s.l. classification was taken into consideration rather than Lu. intermedia s.str. or Lu. neivai, due to the data found in the databases referring to information previous to the distinction of this species complex.
Mean incidence rates were calculated from autochthonous cases reported to the CVE/SES/SP. The dates when clinical manifestations of each case reported between 1998 and 2008 began to occur were considered for these incidences.
Cities were classified based on the magnitude of occurrence of cases as "small magnitude" (occurrence of 1 to 5 cases), "average magnitude" (occurrence of 6 to 20 cases) and "great magnitude" (occurrence of 20 or more cases) and analyzed according to their environmental characteristics, their ATL incidence rates and magnitude.
The figures that show the occurrence of vectors were developed with data from Pessoa and Barretto4 in the 1940s and from entomological surveys conducted by SUCEN between 1985 and 2008, having considered the studies by Marcondes (1996)14 and Andrade-Filho et al. (2003 and 2007)19,20 on Lutzomyia intermedia and Lutzomyia neivai, represented in this study by Lutzomyia intermedia s.l.
This study was conducted with secondary data derived from the SUCEN and CVE/SES/SP and only grouped data were published. The research protocol was submitted to and approved by SUCEN.
Between 1975 and 2008, the CVE/SES/SP recorded 12,978 autochthonous ATL cases distributed in 385 cities, with a predominance of those situated in the areas mostly covered by the Atlantic Forest. From 1975 to 1985, 45 cities were responsible for the recording of 1,281 ATL cases, increasing to 258 cities and 4,093 cases from 1986 to 1995 and to 32.9% of cities affected from 1996 to 2008, thus representing a linear trend of increase in number of cases (r2=0.5243) (Figure 1). There was an increase in the number of cities in the state of São Paulo where 1 to 5 autochthonous cases of ATL were reported. Between 1986 and 1995, cities with 1 to 5 cases represented 58.9% and those with up to 20 cases represented 80.6%; between 1998 and 2008, these percentages were 67.5 and 86.7, respectively. A number higher than 20 cases was observed in 19.4% of the cities in the state from 1986 to 1995 and in 13.3% from 1998 to 2008.
The coefficients of accumulated mean incidence between 1998 and 2008 were calculated and they varied from 0.00 to 152.48 cases/ 100,000 inhabitants, when the highest indices were found in cities mainly situated in the eastern part of the state (Figure 2). The southeastern, northeastern and central-west regions of Brazil contributed with high percentages. In the classification of cities according to the magnitude of occurrence of cases, 67.5% had a "small magnitude", 19.2% had an "average magnitude" and 13.3% had a "great magnitude".
The Lutzomyia intermedia s.l. vector was associated with the majority of entomological surveys conducted by SUCEN. When compared to the distribution of Lu. intermedia made by Pessoa and Barretto (1948)4, an increase in its distribution area can be observed (Figure 3). Between 1998 and 2008, 14,354 Phlebotominae specimens of 16 species of the genus Lutzomyia were collected, mainly represented by Lu. intermedia s.l. (81.25%), Lu. whitmani (7.28%) and Lutzomyia pessoai (3.28%) (Table 1). When the 645 cities of the state and the entomological collections performed between 1985 and 2008 were considered, Lu. intermedia s.l. was recorded in 148 of these cities (22.9%), Lu. whitmani in 111 (17.2%), Lutzomyia fischeri in 102 (15.8%), Lu. migonei in 87 (13.4%) and Lu. pessoai in 66 (10.2%). Lower percentages were obtained for species of minor epidemiological importance.
In possible areas of infection, the presence of only one Phlebotominae species was observed in 41 (6.3%) cities of the state of São Paulo, two sub-species in 33 cities (5.1%), and a number higher than three species in 132 cities (20.5%).
The cross-over between ground cover and geomorphological21 data and case distribution data, according to the magnitude between 1998 and 2008 and distribution of ATL vectors between 1985 and 2008, enabled researchers to observe an increase in high-risk areas.
In the first decades of the 20th century, when the western part of the state of São Paulo was colonized, important endemic areas of ATL appeared, especially in the Alta Sorocabana, Noroeste and Alta Paulista regions22. After this stage, the cases were concentrated in certain areas in a non-homogeneous way. Currently, the epidemiological status of ATL is characterized by the predominance of autochthonous cases with transmission occurring in the entire state and coinciding with the distribution of Phlebotominae vectors.
Higher incidence coefficients have been observed in the southern, eastern, western and southeastern regions of the state of São Paulo. Previously known incidence areas increased and a great number of cases were recorded in new rural areas. The highest incidences of ATL remain restricted to certain areas close to the Atlantic Forest in the state of São Paulo. There was an increase in the number of cities with a low occurrence of cases ("small magnitude"). Cases are concentrated in growing populations, in areas with precarious housing and a low per capita income23 and which are exposed to the vector24, where control strategies must emphasize measures directly associated with the human environment.
The presence of 17 Phlebotominae species indicates a high diversity, probably due to the diverse vegetation and terrain. The climate is a factor that affects the distribution of Lutzomyia species. The rise in global temperature has an impact on climatic variability, enabling an increase in the density of Diptera species with an effect on the increase in ATL cases, which was observed with the El Niño Southern Oscillation (ENSO) in certain places of Colombia25.
When the species found per city of the state are observed, even if they are in the same landscape features, one species or another seems to have a major role in ATL transmission, thus agreeing with data from other authors11,26,27. In the past, during the 1930s and 1940s, ATL transmission was associated with Lu. whitmani, Lu. pessoai and Lu. migonei, species with wild behavior28,29. Currently, L. (V.) braziliensis is found to be associated with a variety of Phlebotominae species with different transmission cycles in many geographic areas, where the vector is present in and around homes and in domestic animal shelters25.
Lu. intermedia s.l. has been pointed out as the most important taxon in the current epidemiological profile of ATL, due to its predominance in altered environments and constant presence in the intra- and peridomicile, corroborating the studies by Shimabukuro et al.30. At that time, Pessoa and Barretto (1948)4 classified the coastal area of the state of São Paulo as an area without human cases or vectors and the Western Plateau as a high-endemicity area, where Lu. whitmani and Lu. pessoai predominate. In the present assessment, Lu. intermedia s.l. was the main species involved in ATL transmission in coastal areas and plateaus. The overlapping of distribution of species in the majority of cities with autochthonous cases of ATL indicates the need to perform longitudinal studies in different places as a strategy to understand the transmission cycles of Leishmania (V.) braziliensis. According to Neves et al.31, it could be assumed that the mere identification of one of the Phlebotominae species of greatest epidemiological importance already represents a risk factor for ATL. In addition, this risk is not increased by the identification of more than one species.
The spatial distribution analysis of species in the state of São Paulo showed wide dispersion, although with a strong concentration in certain areas, enabling areas with lower endemicity or the occurrence of isolated cases to be identified. Phlebotominae species seem to occur in a distribution pattern, according to the natural ground cover, geomorphological aspects, isotherms and precipitation. Although certain wilder species have shown a different distribution pattern in the past and are associated with areas where there used to be woods, species with an endophilic behavior showed slight changes in distribution, when compared to literature data. Areas characterized as of average endemicity by Neves (1999)24 became areas with a great magnitude of cases, including an abundance and diversity of vectors and resulting in the expansion of the ATL transmission area. This increase was also observed in the Pontal do Paranapanema region, in the westernmost part of the state, an area considered to be of low endemicity. There is a considerable level of exposure in this region, associated with farming population settlements that were formed and promoted the adaptation of mammal hosts and vectors to a new environment, resulting in an impact on human health31.
The fact is that the onset of this infection is primarily associated with the migratory process and semi-urbanized areas where the presence of domestic animals seems to play a key role as new hosts of parasites24,31,32. In this case, the infection only needs to enter the peridomestic cycle through synanthropic (or domestic) animals and the disease will occur and increase due to unhealthy and precarious living conditions.
ATL is increasing in the state of São Paulo and the highest incidence rates are found in the Vale do Ribeira region, situated in the southern part of this state33. Although this region includes a great environmental and cultural heritage, it lacks sanitation infrastructure and adequate economic alternatives for sustainable development to enable the rational use of resources. The extensive areas with remnants of Atlantic Forest in the Vale do Ribeira region and the fact that homes are located near the woods have promoted the presence of Phlebotominae species, increasing the probability of autochthonous ATL transmission33.
Although knowledge about the epidemiology and behavior of vectors has been increased, there is much to be investigated in terms of their dispersion and survival mechanisms due to the ecological imbalance. The existence of vectors out of the wilderness represents a chance of dissemination of parasites away from the limits of the natural area of the disease and the occurrence of secondary cycles of Leishmania, which means that several factors translate into the occurrence of cases and dynamics of transmission. This should be investigated to guarantee more adequate and efficient control strategies and protection measures to prevent transmission in the areas emphasized in this study. The diversity of epidemiological and ecological profiles for different regions prevents the adoption of common disease control measures34. Program surveillance and control are based on specific measures for each area, according to the epidemiological situation. In addition, they focus on early diagnosis and adequate treatment of human cases, apart from the identification of the etiological agent present and the primary vector and reduction in the human-vector contact, through the adoption of individual and collective protection measures35.
Enabling the population to understand this is essential to control ATL. When children and teachers are informed, they can disseminate knowledge at home and in the community and perform relevant work to control endemic diseases36.
The importance of reporting ATL cases should be emphasized, especially when considering the need to bring about and implement control measures. This is because the underreporting of cases hinders the understanding of the behavior of the disease in possible areas of transmission and its follow-up in areas already known, in addition to causing distortions in terms of incidence rates. With regard to the distribution of ATL vectors, knowledge about high-risk areas and the dissemination of such knowledge provide support to the surveillance of this disease.
Authors declared that there were no conflicts of interest.
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Correspondência: Received: 04/14/11
Rubens Antonio da Silva
Departamento de Combate a Vetores
Superintendência de Controle de Endemias
Secretaria de Estado da Saúde de São Paulo
Rua Paula Sousa 166, 1º andar, Luz
CEP 01027-000 São Paulo, SP.
Final version: 01/11/12