INTRODUCTION
American cutaneous leishmaniasis (ACL) is an infectious disease affecting the skin and mucosa. It is caused by protozoa of the genus Leishmania and is transmitted by different species of phlebotomine sandflies1.
The incidence of ACL is increasing in Latin America, especially in Brazil, where 256,587 cases were recorded from 2000 to 2009. In this period, 82,510 (32.2%) cases were reported in the northeastern region of the country, of which 32,548 (39.4%) came from the State of Maranhão2.
The State of Maranhão is located among three biomes that display variations in physiographic, climatic and ecosystem diversity. These regions are of critical importance in the epidemiology of ACL, as they are highly endemic for the disease. The Cerrados of central Brazil are situated in the eastern portion of this region, while Caatinga ecosystems are found to the northeast and the Amazonian forest to the west3.
Several researchers have conducted spatial analyses of the dynamics of infectious diseases4,5. The analysis of relative risk (RR) over space and time has received a great deal of attention in epidemiological studies over the last few decades. Many studies assume that RR is composed of several random components, and these components explain different variations related to risk, such as temporal and spatial effects4,6,7.
In this study, data on ACL from 2000-2009 were analyzed. The ACL data were expected to be correlated in space due to exposure to common environmental characteristics that influence transmission similarly in neighboring areas. The standard statistical methods assume independent observations. To take spatial correlations into account, Bayesian spatiotemporal models8,9 were developed to evaluate the spatiotemporal autocorrelation of the disease. Due to the large number of model parameters, a Markov Chain Monte Carlo (MCMC) simulation was used for model fitting.
This study aimed to assess the spatiotemporal distribution of ACL in counties located along road and railway corridors in the State of Maranhão, Brazil.
METHODS
We conducted a retrospective ecological study describing the spatiotemporal distribution of ACL cases in 61 counties in the State of Maranhão, Brazil, from 2000 to 2009. Sixty-one counties located along the main road and railway corridors were selected as the study sites: I – São Luis-Timon (construction started in 1895): 27 counties along roads 135 and 316 and the line of the Northeastern Railway Company; II – São Luis-Açailândia (beginning of the 1980s): 20 counties along roads 135 and 222 and the line of the Carajás Railroad; and III – Açailândia-Carolina (beginning of the 1980s): 14 counties along road 010 and the North-South Railroad (Figure 1).

FIGURE 1 Map of the State of Maranhão, Brazil, showing the studied counties located along the road and railway corridors, 2000-2009.
The ACL data were obtained from the Ministry of Health of Brazil and the demographic data from the Brazilian Institute of Geography and Statistics (IBGE).
An initial descriptive analysis of ACL incidence was conducted. Bayesian spatiotemporal Poisson regression models were constructed using WinBUGS software10. The response variable, yit, was the number of ACL cases reported in county i in year t (for i = 1, 2 …, 61 and t = 1, 2 …, 10). We assumed that yit followed a Poisson distribution with a mean of eitθit, where eit is the number of cases expected in county i at time t, and θit is the area-specific risk rate in county i at time t.
The number of expected cases, eit, between 2000 and 2009 for each county was calculated with the equation , where pit is the population in county i at time t.
In the disease-mapping literature, estimates of RR are obtained through a maximum likelihood estimator, which, in this case, is given by θit = yit/eit. Estimates of θit based on maximum likelihood estimators are biased, especially when the disease is rare, or the region of interest has a small population8.
In the present study, the spatiotemporal model considers log(θit) = βt + bit,, where the temporal effect is given by βt = βt – 1 + wt, and wt is a normally distributed random error with a mean of zero and an unknown variance. This model assumes that the RR is related to both the temporal effect βt and spatiotemporal effect bit.
Prior distributions must be specified for the model parameters. We modeled the random effects terms, bit, as a conditional auto-regressive (CAR) model with variance of . For wt, we assumed an a priori non-informative Gaussian distribution with a mean of zero and an unknown variance of . Additional references using CAR prior distributions for disease mapping are provided by Bernardinelli et al.6,11,12. Inverse-gamma prior distributions were specified for all of the variance parameters, with a shape of a=1 and a scale of b=1.
We estimated the parameters through an MCMC simulation. Three parallel chains were run with different initial values for the parameter estimates. A burn-in of 5,000 interactions, followed by 10,000 interactions was allowed, and the values of the main parameters were stored. Terra View software, version 3.5, was used for mapping the resulting posterior distribution of the estimated RR parameters.
RESULTS
From 2000 to 2009, there were 13,818 cases of ACL recorded, including 4,571 cases along Line I (169 cases/county), 7,137 cases (357 cases/county) along Line II and 2,110 cases (151 cases/county) along Line III.
The annual incidence of ACL is shown in Figure 2. Since 2000, a gradual decrease in ACL incidence has been reported in the studied areas. This pattern of occurrence was common to the three lines.

FIGURE 2 Incidence of American cutaneous leishmaniasis cases along road and railway corridors in the State of Maranhão, Brazil, 2000-2009.
The RRs for each of the 61 counties during 2000-2009 are provided in Figure 3 and Table 1. The counties along Line II always presented a high risk. However, the eastern region (Line I) of the state showed a significant decrease in risk over the study years. Along Line III, different risks were observed in the counties.

FIGURE 3 The relative risk of American cutaneous leishmaniasis in the counties located along road and railway corridors in the State of Maranhão, Brazil, 2000-2009.
TABLE 1 – Relative risk of American cutaneous leishmaniasis in the cities located along the road and railway corridors, State of Maranhão, Brazil, 2000-2009.
County | 2000 | 2001 | 2002 | 2003 | 2004 | 2005 | 2006 | 2007 | 2008 | 2009 |
---|---|---|---|---|---|---|---|---|---|---|
Line I | ||||||||||
Rosário | 0.598 | 0.071 | 0.245 | 0.128 | 0.485 | 1.407 | 1.792 | 1.260 | 1.933 | 3.069 |
Alto Alegre do Maranhão | 0.069 | 0.261 | 0.615 | 0.415 | 0.741 | 2.297 | 6.733 | 4.998 | 3.903 | 4.094 |
Cantanhede | 1.089 | 1.312 | 0.456 | 0.662 | 0.595 | 1.251 | 0.585 | 0.427 | 1.659 | 1.957 |
Codó | 0.713 | 1.116 | 1.093 | 1.100 | 1.192 | 1.139 | 1.035 | 0.783 | 1.063 | 1.159 |
Gonçalves Dias | 0.357 | 0.485 | 0.953 | 1.428 | 3.316 | 1.395 | 4.193 | 3.176 | 3.203 | 4.196 |
São Luís Gonzaga do Maranhão | 0.381 | 0.192 | 0.574 | 0.824 | 0.527 | 2.208 | 0.953 | 0.722 | 1.203 | 1.144 |
São Mateus do Maranhão | 0.063 | 0.170 | 0.143 | 0.114 | 0.133 | 0.195 | 0.364 | 0.222 | 0.247 | 0.201 |
Timbiras | 0.209 | 0.491 | 0.606 | 0.527 | 0.970 | 1.170 | 1.244 | 0.833 | 0.304 | 0.948 |
Timon | 0.121 | 0.180 | 0.317 | 0.222 | 0.243 | 0.190 | 0.144 | 0.108 | 0.287 | 0.268 |
Santa Rita | 0.141 | 9.080 | 0.464 | 0.185 | 0.734 | 0.441 | 0.261 | 0.188 | 0.402 | 0.508 |
São Luis | 0.001 | 0.033 | 0.047 | 0.032 | 0.084 | 0.058 | 0.093 | 0.063 | 0.120 | 0.082 |
Miranda do Norte | 0.377 | 0.185 | 0.381 | 2.434 | 1.425 | 0.647 | 0.872 | 0.647 | 0.478 | 0.412 |
Peritoró | 0.217 | 0.438 | 1.190 | 0.555 | 0.581 | 0.427 | 1.164 | 0.865 | 1.739 | 0.802 |
Lago Verde | 0.036 | 0.118 | 0.123 | 0.206 | 0.131 | 0.128 | 0.403 | 0.344 | 0.214 | 0.144 |
Conceição do Lago-Açu | 0.033 | 0.099 | 0.132 | 0.189 | 0.214 | 0.215 | 0.257 | 0.288 | 0.242 | 0.162 |
Coroatá | 0.140 | 0.743 | 0.663 | 0.769 | 0.815 | 0.419 | 0.748 | 0.550 | 0.815 | 0.714 |
Bacabal | 0.040 | 0.086 | 0.073 | 0.084 | 0.102 | 0.104 | 0.193 | 0.103 | 0.470 | 0.200 |
Bacabeira | 0.043 | 0.099 | 0.099 | 0.229 | 0.175 | 0.279 | 0.239 | 0.174 | 0.666 | 0.730 |
Anajatuba | 0.149 | 0.097 | 0.264 | 0.139 | 0.190 | 0.356 | 1.146 | 0.850 | 0.633 | 0.226 |
Aldeias Altas | 2.938 | 2.740 | 1.996 | 1.654 | 2.886 | 3.496 | 3.098 | 2.365 | 0.626 | 1.608 |
Capinzal do Norte | 1.020 | 0.633 | 0.643 | 1.776 | 0.539 | 0.241 | 0.463 | 0.349 | 1.167 | 0.451 |
Caxias | 4.867 | 3.098 | 2.084 | 1.012 | 1.652 | 1.781 | 0.781 | 0.569 | 1.154 | 0.661 |
São João do Soter | 1.208 | 1.930 | 1.660 | 4.004 | 2.615 | 2.352 | 2.378 | 1.795 | 1.399 | 0.689 |
Itapecuru Mirim | 1.068 | 1.378 | 0.808 | 0.636 | 1.362 | 2.207 | 0.627 | 0.415 | 1.427 | 0.933 |
Pirapemas | 0.442 | 0.700 | 0.357 | 0.316 | 0.576 | 0.736 | 0.829 | 0.457 | 0.486 | 0.323 |
Lima Campos | 0.673 | 1.103 | 1.634 | 2.886 | 0.495 | 0.637 | 1.452 | 1.103 | 1.111 | 0.652 |
Matões do Norte | 0.297 | 0.882 | 2.516 | 0.454 | 0.258 | 0.528 | 0.563 | 0.399 | 0.334 | 0.295 |
Line II | ||||||||||
Açailândia | 2.002 | 3.869 | 2.703 | 2.707 | 3.938 | 2.723 | 3.026 | 3.025 | 2.225 | 3.390 |
Alto Alegre do Pindaré | 0.139 | 1.319 | 1.579 | 1.102 | 1.058 | 2.281 | 2.947 | 2.736 | 5.620 | 7.780 |
Arari | 0.055 | 0.081 | 0.098 | 0.123 | 0.129 | 0.125 | 0.237 | 0.176 | 0.221 | 0.154 |
Bela Vista do Maranhão | 0.035 | 0.097 | 0.371 | 0.436 | 1.435 | 0.679 | 0.495 | 0.683 | 1.005 | 0.338 |
Bom Jardim | 1.077 | 1.509 | 1.497 | 1.449 | 2.200 | 1.611 | 2.311 | 1.686 | 2.947 | 2.551 |
Cidelândia | 2.285 | 0.830 | 2.537 | 1.468 | 1.149 | 1.615 | 2.221 | 1.036 | 5.947 | 3.629 |
Igarapé do Meio | 0.039 | 0.120 | 0.282 | 0.712 | 0.232 | 1.013 | 0.276 | 0.393 | 0.329 | 0.243 |
Monção | 0.042 | 0.087 | 0.174 | 0.239 | 0.299 | 0.232 | 0.317 | 0.286 | 0.296 | 0.227 |
Pindaré-Mirim | 0.067 | 0.487 | 0.700 | 0.348 | 0.488 | 0.851 | 0.852 | 0.839 | 0.847 | 0.765 |
Pio XII | 0.038 | 0.159 | 0.440 | 0.174 | 0.238 | 0.378 | 0.320 | 0.728 | 0.201 | 0.143 |
Santa Inês | 0.037 | 0.311 | 1.110 | 0.532 | 0.470 | 0.632 | 0.371 | 0.769 | 0.437 | 0.410 |
São Pedro da Água Branca | 1.080 | 0.128 | 0.876 | 1.087 | 2.880 | 1.223 | 0.298 | 1.190 | 1.926 | 1.296 |
Satubinha | 0.035 | 0.087 | 0.197 | 0.176 | 0.554 | 0.357 | 0.256 | 0.315 | 0.327 | 0.239 |
Tufilândia | 0.189 | 0.755 | 1.156 | 0.883 | 1.261 | 0.851 | 2.043 | 3.763 | 1.562 | 8.660 |
Vila Nova dos Martírios | 1.369 | 0.609 | 0.395 | 1.639 | 1.768 | 0.770 | 2.059 | 0.648 | 1.132 | 3.330 |
Line II | ||||||||||
Vitória do Mearim | 0.031 | 0.060 | 0.081 | 0.287 | 0.392 | 0.146 | 0.210 | 0.209 | 0.310 | 0.131 |
Bom Jesus das Selvas | 4.472 | 1.867 | 5.459 | 5.301 | 4.644 | 6.323 | 5.631 | 5.960 | 3.463 | 0.952 |
Buriticupu | 12.910 | 7.875 | 11.98 | 10.13 | 6.431 | 7.162 | 4.172 | 4.636 | 2.504 | 2.609 |
Itinga do Maranhão | 7.582 | 5.025 | 3.944 | 5.035 | 8.994 | 4.460 | 6.334 | 8.221 | 6.615 | 7.347 |
Santa Luzia | 4.196 | 3.119 | 2.986 | 5.171 | 2.376 | 3.358 | 1.677 | 4.797 | 4.282 | 3.582 |
Line III | ||||||||||
Campestre do Maranhão | 0.487 | 0.531 | 0.414 | 0.886 | 0.407 | 0.605 | 0.878 | 1.067 | 0.456 | 0.622 |
Carolina | 0.539 | 0.060 | 0.203 | 0.428 | 1.035 | 0.435 | 3.500 | 1.636 | 3.275 | 1.200 |
Davinópolis | 0.949 | 2.847 | 2.079 | 3.875 | 0.407 | 1.720 | 1.558 | 1.250 | 1.423 | 1.527 |
Governador Edson Lobão | 1.557 | 1.675 | 1.386 | 0.860 | 0.588 | 0.987 | 1.322 | 0.778 | 2.188 | 2.777 |
Imperatriz | 0.659 | 0.948 | 0.930 | 0.749 | 0.995 | 0.861 | 1.034 | 1.160 | 1.001 | 0.769 |
João Lisboa | 0.694 | 0.463 | 1.591 | 2.282 | 1.694 | 1.992 | 1.890 | 2.532 | 1.057 | 0.932 |
Lajeado Novo | 1.229 | 0.581 | 0.581 | 3.144 | 1.641 | 0.779 | 2.329 | 1.140 | 1.056 | 3.198 |
Montes Altos | 1.007 | 1.025 | 3.237 | 4.434 | 3.446 | 2.744 | 10.570 | 3.725 | 2.280 | 3.450 |
Porto Franco | 0.460 | 0.420 | 0.628 | 0.838 | 0.824 | 1.076 | 0.852 | 1.245 | 1.033 | 1.169 |
Ribamar Fiquene | 0.556 | 0.412 | 0.741 | 1.517 | 1.095 | 0.794 | 1.609 | 1.127 | 1.432 | 2.425 |
São João do Paraíso | 0.173 | 0.228 | 0.342 | 0.944 | 0.577 | 0.283 | 0.690 | 0.527 | 1.601 | 10.41 |
Senador La Rocque | 0.641 | 1.645 | 3.173 | 5.899 | 3.006 | 2.904 | 1.541 | 2.937 | 2.898 | 2.239 |
São Francisco do Brejão | 7.120 | 2.991 | 2.608 | 1.573 | 1.376 | 0.844 | 2.602 | 3.381 | 1.574 | 1.599 |
Estreito | 0.538 | 0.292 | 0.520 | 0.732 | 0.810 | 1.487 | 1.426 | 0.958 | 0.343 | 0.563 |
Source: Secretary of Health Surveillance/Ministry of Health of Brazil.
Throughout the study period, the RR increased in 77% of counties, decreased in 18% and was maintained in only five counties.
DISCUSSION
Recent advances in techniques and computer-based programming have helped scientists and researchers monitor environmental and ecological factors affecting the spatial and temporal distribution of several vector-borne diseases, including malaria, leishmaniasis and schistosomiasis, among other diseases7−9,13.
The Bayesian model employed here provided an estimate of the RR of ACL in the examined counties during the study period. The epidemiologic data indicated a significant decrease in the incidence of ACL over the ten years addressed in this study. The examined counties were situated in an historical area for ACL transmission and displayed incidences ranging from 7.36 to 241.45/100,000 inhabitants14,15.
The area with the highest incidence of ACL was located in the western region of the state (Line II), which is under the influence of the Amazon rainforest and is known as an endemic disease area in Brazil14,15. The climate and vegetation of this forest favor a high diversity of vector species, reservoirs and etiological agents16−18. The phlebotomine fauna found in this area are quite diverse, with an abundance of L. whitmani, L. migonei, L. umbratilis and L. complexa being observed14,19,20.
The eastern region of the state (Line I) is also under the influence of the Amazon forest, combined with the transitional palm forest and Cerrado moving from west to east. These characteristics may explain why the incidence found in this region is higher than that recorded in the southwest of the state, which is dominated by Cerrado formations, as the climate is drier in the south21,22.
Studies have shown that many species of phlebotomine ACL vectors previously found in wild environments19,20 are encroaching on rural and peri-urban areas, where they are becoming infected byLeishmania spp.17,23.
The first records of ACL in Maranhão come from the late 1970s from an outbreak detected in Buriticupu15on the Amazon side of the state. A number of outbreaks recorded in Maranhão, São Paulo and Bahia were associated with the introduction of roads and railway lines in forest areas24,25, and we believe the same phenomenon may have occurred along road and railway Line I. However, this line is much older and has existed for more than a century with no record of an infection. Thus, it is possible that the lack of cases reported in association with this line resulted from the absence of disease specialists at the time.
This hypothesis finds support in current records of autochthonous cases of ACL in urban areas of Caxias26, which suggest a long-term adaptation process among phlebotomine sandflies (L. cortelezii, L. evandroi, L. goiana, L. intermedia, L. lenti, L. longipalpis, L. longipennis, L. squamiventris, L. termitophila, and L. whitmani) in these environments. This phenomenon was previously observed in an entomological survey conducted in several counties along this road and railway line27. However, such adaptation has not yet been detected on the Amazonian (west) side, where ACL remains rural or periurban27,28.
Given the above findings, it is presumed that the studied road and railway lines have increasingly been drawing populations from Maranhão and other states from different regions in the country. The northwest road and railway line receives migrants from Pará, Tocantins and other Amazon states, whereas the northeast road and railway line mainly receives migrants from the States of Piauí and Ceará but also from other northeastern States and Minas Gerais. Thus, these lines facilitate the transmission of ACL in the oldest settled areas, such as the area along road and railway Line I receiving a large population flow from the northeastern states, as well as areas settled more recently, including along access routes to the Amazon states and the central region of Brazil.
In Brazil, health records are critical sources of data for studies. However, the availability and quality of the data are matters of great concern. For example, the lack of coverage of the entire population and diagnostic errors can affect the quality of the data and lead to underreporting. Reliability and validity are essential in large database studies to accurately assess the possibility of bias in spatial research based on secondary data29.
Nevertheless, the results of this study can be interpreted despite their limitations and potential biases. First, the incidence rates of ACL are based on secondary data, which may underestimate the true incidence due to underreporting. A second potential problem was the failure to consider socioeconomic and environmental indicators given the difficulty of obtaining such data29.
To better understand the influence of roads on the epidemiological profile of this disease, further research will be required to identify variables that can contribute resolving the complex factors contributing to disease transmission.
Road and railway corridors may play an important role in the spread of LTA by facilitating the movement of populations with varying risks of contracting the disease, thus influencing its epidemiology.
The data presented and discussed in this report allow us to conclude that although there was a decrease in the incidence of ACL over the study period, the risk of contracting the disease remains in all of the studied municipalities. Therefore, preventive measures implemented by the Unified Health System should be directed towards the control of disease expansion.