REVIEW REVISÃO

 

Remote sensing as a tool to survey endemic diseases in Brazil

 

O sensoriamento remoto como ferramenta de vigilância em endemias brasileiras

 

 

Virginia Ragoni de Moraes CorreiaI, II; Marilia Sá CarvalhoII; Paulo Chagastelles SabrozaII; Cíntia Honório VasconcelosIII

IDivisão de Processamento de Imagens, Instituto Nacional de Pesquisas Espaciais, São José dos Campos, Brazil
IIEscola Nacional de Saúde Pública, Fundação Oswaldo Cruz, Rio de Janeiro, Brazil
IIIDivisão de Sensoriamneto Remoto, Instituto Nacional de Pesquisas Espaciais, São José dos Campos, Brazil

Correspondence

 

 


ABSTRACT

The objective of this study, based on a systematic literature review, is to present the characteristics and potentialities of remote sensing as a useful environmental surveillance tool for applied research in the control of endemics in Brazil. Onboard satellite sensors allow for monitoring the territory, furnishing spatial and temporal information on various scales and regions in the electromagnetic spectrum. Based on the literature review on the application of this technology to the study of endemics and the identification of the potential of new sensors with better spectral, spatial, and temporal resolutions, this study highlights perspectives for the use of remote sensing in the study of important endemics for Brazil.

Key words: Communicable Diseases; Epidemiologic Surveillance; Review Literature


RESUMO

O objetivo deste trabalho é, a partir de revisão bibliográfica sistemática, apresentar as características e potencialidades do remote sensing como ferramenta de vigilância ambiental útil para pesquisas aplicadas ao estudo e controle de endemias brasileiras. Os sensores a bordo dos satélites permitem monitorar o território fornecendo informação espacial e temporal em várias escalas e regiões do espectro eletromagnético. Baseado na revisão bibliográfica sobre a aplicação dessa tecnologia no estudo de endemias, e na identificação do potencial dos novos sensores, com melhores resoluções espectrais, espaciais e temporais, este trabalho aponta perspectivas para o uso do Sensoriamento Remoto no estudo de endemias importantes para o Brasil.

Palavras-chave: Doenças Transmissíveis; Vigilância Epidemiológica; Literatura de Revisão


 

 

Introduction

Recent environmental and ecological changes within a context of widespread increased social vulnerability, associated with the persistence of inadequate living conditions, have caused an impact on the distribution pattern of diseases. These environmental, economic, and social changes increase the epidemiological complexity, favoring the emergence of new diseases and the reemergence of old endemics, traditionally related to rural areas and currently occurring in new environments, as in the case of visceral leishmaniasis 1,2,3. These questions have motivated health-related organizations, and particularly international agencies like the World Health Organization (WHO), to pursue the development of new surveillance techniques and models in which the environmental issue is fundamental 4.

Remote sensing (RS) ­ a technology capable of acquiring information on the Earth's surface without any contact ­ allows systematic and regular monitoring of the Earth's environmental conditions, furnishing large amounts of spatial and temporal data and the possibility of extracting climatic and ecological information. Such information, together with appropriate field studies, can be used to identify and map the potential habitats of parasites and disease vectors; predict alterations in vector and parasite populations, monitoring quantitative and qualitative alterations in the respective habitats; and plan control programs, indicating areas of greater and lesser risk of the disease 5.

The environmental factors most closely related to vector-borne endemics and amenable to observation from spatial platforms include: temperature, water, soil moisture, plant cover conditions, deforestation, urban characteristics, ocean color, and topography 6.

Recognizing the potential of RS as well as its scarce utilization in Brazil, a review was conducted on the scientific knowledge acquired from applications of this technique to the study of endemic (and particularly vector-borne) diseases. The study attempts to identify possibilities for the use of this technology as a tool to support the study and control of the most frequent endemics in Brazil.

The article is developed along three main lines:

• Description of the main characteristics of sensors, seeking to provide the basis for discussing their use;

• The "state of the art" in the use of remote sensing applied to endemics;

• For each endemic, a description of its pattern, risk areas, information that the images can provide, and the satellites/sensors that can be utilized.

 

Principal sensors and their characteristics and applications

RS essentially measures the energy reflected or emitted in distinct and specific wavelengths in the electromagnetic spectrum, using sensors, usually on board satellites. When the objective of the monitoring is environmental, the visible, infrared, and microwave regions of the spectrum are used 7,8.

RS systems can be classified as active or passive. In active systems, for example radar,Radio Detection and Ranging, the sensor emits a flow of radiation in the microwave spectral range which interacts with targets on the Earth's surface, and the reflected portion is captured by the sensor. The principal advantages of radar are that: it operates both daytime and nighttime; cloud cover does not impede its use; and it detects different textures and slopes. Passive systems record environmental energy ­ light and heat ­ reflected and emitted, captured by the sensor. The TM (Thematic Mapper) sensor from the LANDSAT (Land Satellites) series and the HRV (High Resolution Visible) sensor from SPOT (Satellite Pour l`Observation de la Terre) are examples of passive sensor systems 7.

The different types of resolution that are characteristic of each sensor define the information content for each scene obtained.

Spectral resolution refers to the spectral range of each band in a given sensor and indicates the energy sample frequency. Since the targets display different responses in each of these spectral ranges, this information is used to identify such targets. For example, in an area of vegetation one observes a high reflectance value in the near-infrared region and a low value in the visible red band. Spatial resolution can be defined as the smallest possible area of terrain that can be individualized. Temporal resolution indicates the time interval between two satellite passes over the same point on Earth 9,10.

Table 1 shows the principal existing RS systems and their characteristics. The inclusion of the LANDSAT ETM+ sensor, out of operation since May 2003, is due to the large mass of data generated during its active period, from 1999 to 2003.

 

 

In the first contact with an RS image, the user utilizes such elements as tone, shape, size, pattern, texture, shadow, and association to interpret it. One can distinguish an urban area from a rural one, a more or less dense urban zone, crop areas from natural areas, and the rough texture of forest canopies from a smooth texture such as asphalt, crop fields, and pasture or grassy areas 7,11.

As for the choice of images, one should use those with the most adequate spatial, spectral, and temporal resolutions for the study. In relation to spatial resolution, what is essential is to evaluate the size of the object one wishes to map. In the identification of small agricultural areas, trees, buildings, rooftop characteristics, and distances between residences, one can use a maximum 5-meter resolution. A 15-meter resolution is capable of detailing forest areas or identifying city blocks, while 20 to 30-meter resolutions are ideal for identifying urban areas, roads, airports, and forest and agricultural areas, as well as characterizing land use. To detect floodable areas one can use spatial resolutions ranging from 10 to 100 meters, depending on the study area. A 1,000-meter resolution can be used to quantify vegetation and temperature 6.

The images furnished by LANDSAT and SPOT satellites provide a scale of details that is impossible to obtain from the NOAA (National Oceanic and Atmospheric Administration) weather satellite. However the latter has high temporal resolution, allowing the acquisition of images from the same region with a 12-hour frequency, while LANDSAT and SPOT have temporal resolutions of 16 and 26 days, respectively. When the study is done on a regional or continental scale, one normally uses images that cover larger areas. In this case, one can use NOAA or TERRA satellite images. The same area would require a larger number of LANDSAT images, involving an additional cost.

IKONOS and QUICKBIRD images, whose spatial resolution is better, can be interesting for the study of densely populated urban areas. In tropical areas with heavy cloud cover, radar images can be useful. In addition, active microwave sensors are particularly valuable for monitoring flooded areas.

In addition to the spatial and temporal resolution, one should be alert to the spectral range that best identifies the target. Flooded forests can be detected using the SAR-L band from JERS-1 radar 12; for urban characteristics one can use the panchromatic band of SPOT or IKONOS 13. Ecotones can be best identified using bands in the spectrum between 0.4 and 1.3µm, which includes visible and near-infrared, utilizing the LANDSAT, SPOT, or IKONOS satellite, depending on the desired detail 6.

Factors related to endemics, such as the effects of climatic variations on vegetation, urban growth, and deforestation, require temporal follow-up. A combination of sensors from different satellites, like a fusion of radar and optical images, can be used in complementary fashion 14.

Imaging processing techniques based on spectral responses can generate new information 8,9. For example, using mixture modeling, one can create bands for the proportion of water, soil, and vegetation 15,16. Operation of NDVI, Normalized Difference Vegetation Index, has also created a biomass information band that can indicate possible habitats of disease vectors and reservoirs. The operation, which transforms the spectral components represented in the RGB (Red, Green, Blue) color space into a system that furnishes information on intensity, hue, and saturation, can be useful for image fusion, thus allowing to use SPOT-PAN spatial resolution while keeping LANDSAT-TM spectral resolution 17.

TERRA, the Latin term for "Land", a land observation satellite launched by NASA in 1999, has great potential for studying endemics. This satellite has various sensors, including MODIS (Moderate Resolution Imaging Spectroradiometer) and ASTER (Advanced Spaceborne Thermal Emission and Reflection Radiometer). The former has 36 spectral bands with 250, 500, and 1,000-meter resolutions and a 2-day temporal resolution. The latter has three 15-meter resolution bands in the 0.5-0.9µm region, six 30-meter resolution bands in the 1.6-2.5µm region, and five 90-meter bands in the 8-12µm region, with a 16-day temporal resolution These sensors are capable of monitoring land environmental factors in various resolutions 7,10.

In addition to the sensors already in operation, space agencies are expected to launch more than 80 missions by the year 2010, with instruments capable of measuring environmental change parameters with improved spectral, spatial, and temporal resolutions 6. The literature related to RS application in the study of vector-borne diseases has grown, and new research perspectives are opening up with the emergence of sensors with improved resolutions.

 

Systematic review

The systematic literature review covered the period from 1996 to 2002, searching the following sources: MEDLINE (Medical Literature, Analysis, and Retrieval System Online), using "remote sensing" as the keyword; articles referred to in these publications when not indexed in MEDLINE; the Internet, especially the CDC website (Centers for Disease Control and Prevention) 18 and CHAART (Center for Health Applications of Aerospace Related Technologies ­ http://www.geo.arc.nasa.gov/sge/health); SciELO (Scientific Electronic Library Online ­ http://www.scielo.br); and the thesis/dissertation database of CAPES (Coordenação de Aperfeiçoamento de Pessoal de Nível Superior ­ http://www.ged.capes.gov.br/agdw/silverstream/pages/frPesquisaTeses.html).

Table 2 provides a summary of the result of the systematic review, the reference for which was the pioneering work of Beck et al. 9. Several contributions 19,20,21,22,23,24,25,26,27,28 were not included, since they were already reviews themselves.

 

 

Among the various sensors used, including in the Brazilian studies, there was a predominance of AVHRR (NOAA) and TM (LANDSAT), possibly because they are the oldest and with a broad historical series. There are still no studies applied to health using the high-resolution images from the QUICKBIRD or IKONOS satellites. As for radar images, no references were found, although they are mentioned in some articles as a potential resource for detecting floodable areas, possible habitats for mosquito larvae 25,28.

The review showed that most applications refer to the continental scale, with few on urban areas. Most information obtained by satellite is correlated to vegetation, utilizing NDVI, an index obtained from operations with spectral bands. For example, in the case of NOAA, utilizing bands 1 and 2 from the AVHRR sensor, one can highlight the vegetation through the following operations: band2/band1 or (band2-band1)/band2+band1. These operations can also be used based on LANDSAT, with the same objective, using bands TM4 and TM3. The enhancement of vegetation using these operations is due to the high spectral response of vegetation as compared to the soil in band 4 of the TM sensor and band 2 of AVHRR 29,30.

The methodologies correlating this measurement with target epidemiological indicators varied considerably in the studies. Werneck & Maguire 31 use NDVI as the independent variable in a mixture modeling in order to explain the incidence rate for visceral leishmaniasis in census tracts in the city of Teresina, Piauí. In the State of Bahia, Bávia et al. 32 use a multiple regression model in which NDVI is one of the explanatory variables. Thompson et al. 33 utilize NDVI as the dependent variable in a logistic regression to study the probability of occurrence of the vector Plebotomus orientalis in various locations in Sudan, Africa. Kitron & Kazmierczak 34 use the spatial autocorrelation measurement Moran's I to identify the degree of spatial grouping of cases of Lyme disease, ticks, and vegetation (NDVI) in Wisconsin, USA.

Considering the number of references (Table 2), malaria has been the most extensively studied endemic in this environmental context, utilizing a variety of high and low-resolution sensors. Risk of malaria infection, its spread, and seasonality are determined by the combination of human exposure, high vector density, the time the parasite takes to develop in the mosquito, vector survival rate, parameters influenced by meteorological variables such as temperature, precipitation, and relative humidity, deforestation, and bodies of water, which can be mapped by RS directly or using measures such as the vegetation index, surface temperature, and cloud temperature 35. Despite this relevance of this endemic in Brazil, only three studies were located on RS and malaria 36,37,38.

Of the six articles found on leishmaniasis (Table 2), five apply to Brazilian regions. Three of these article refer to tegumentary leishmaniasis (TL) in Southeast Brazil 39,40,41 and the others to visceral leishmaniasis (VL) in the Northeast. Of the latter, one deals with climatic and demographic determinants of VL in the town of Canindé, Ceará 42; another is an ecological study of VL in the city of Teresina, Piauí 31. The CAPES thesis/dissertation database included three dissertations utilizing LANDSAT images to study tegumentary leishmaniasis 41,43,44.

Schistosomiasis is an important endemic in various tropical and subtropical countries and has been extensively studied, with a predominant utilization of the AVHRR sensor (Table 2). The number of references to schistosomiasis is due mainly to a special issue of Acta Tropica, dedicated to the study of the disease with a focus on the use of RS and GIS techniques. One of the articles presents an application in the State of Bahia 32 in which the authors used products derived from the AVHRR sensor, vegetation index, and diurnal temperature difference, to verify the relationship between the environment and density of schistosomiasis distribution. The authors go on to utilize these factors in a forecasting model to calculate the environmental risk of the disease in the municipalities in the State of Bahia. The authors used the SPRING-GIS software to develop and analyze maps for NDVI and dT (diurnal temperature difference).

 

Environment and endemics ­ challenges

Table 3, based on the description of possible ecological, socio-environmental, and soil-use characteristics related to the occurrence of endemics in Brazil, attempts to systematize the potential use of RS, discussing the variety of favorable environments. This table should be read as a challenge for researchers, raising hypotheses that orient this type of work, without the aim of exhausting the subject. In some cases the table categorizes the epidemiological pattern for the occurrence of the endemic in sub-groups in order to facilitate the characterization of environmental aspects detectable by RS. In all the references to specific sensors, the most accessible and lowest-cost sensor was prioritized, although it is possible to use finer resolutions. Each object of study has its specificities, and due to the diversity of factors involved, it is often necessary to use various sensors with different resolutions. In addition, complementary data from other sources included in a Geographic Information System may be necessary. Therefore, the objective is not to limit the applications to specific sensors, but to convey the idea of plurality, possibilities, and also limitations. The principal aspects of some of these endemics are listed below.

In mapping Chagas disease transmission areas, the land occupation pattern can be identified by using images with a resolution of up to 30 meters, allowing the identification of neighborhoods and estimated distances to breeding sites. In the case of schistosomiasis, mapping bodies of water in the middle of natural vegetation is of fundamental importance. Various sensors, including microwave sensors, can contribute to the study and choice of the sensor and should prioritize the size of these bodies of water. Imaging in this case helps detect risk areas and can support control measures by estimating the size of surfaces for use of molluscicide.

Sylvatic yellow fever is of great importance due to its high case fatality rate. One of the fundamental questions in this case is the risk of reaching populations in areas lacking vaccine coverage, which depends on the occurrence of monkey epizootics in these regions. Images can help detect forest corridors through which populations of infected monkeys can migrate. In this case, the images furnished by LANDSAT, SPOT, CBERS-CCD, and TERRA-ASTER sensors can be useful by identifying fragments of forests.

Leptospirosis occurs in Brazil with two distinct profiles: urban, related to areas with a high density of rats, with outbreaks following floods, and rural. The most susceptible locations are thus areas that concentrate water and mud. Although civil defense in cities has usually defined the potentially floodable areas, the definition is relatively gross. Images can help identify flooded areas and, together with slope information, more precisely map the risk areas. In this case the disease's seasonality also calls for periodic imaging. Radar images, although useful in slope identification and when there is cloud coverage, would contribute little to more detailed mapping of urban areas due to interference by the signal reflection on various other surfaces (European Space Agency ­ http://www.envisat.esa.int/dataproducts/asar). In this type of application, the images should display high spatial and temporal resolution and be available soon after the rain, in order to allow mapping of the wet flooded areas. Ideally, these images would be available as soon as they are acquired, like those used for weather forecasting, but this is not the case at present.

Visceral leishmaniasis was formerly transmitted mainly in forest areas or concentrated in small rural settlements, with the fox as the main reservoir. More recently VL has occurred in medium-sized Brazilian cities with low plant cover and the dog as the main reservoir, with the disease related to the organization and expansion of urban space 31. LANDSAT, SPOT, and IKONOS sensors can be used to detect areas of vegetation, the limits between forests and urban areas, areas of vegetation within cities, the proximity between forests and residences, and the housing quality and pattern.

Two patterns of malaria occur in Brazil, and one can use images to detect deforested areas, bodies of water, expansion of the urban grid, areas of vegetation, and other characteristics that can point to possible resting and breeding sites for the mosquito vector. Radar images show promise for studying this endemic, complementing information in areas where the responses to optic sensors have limitations.

Tegumentary leishmaniasis, due to the complexity of its cycle, was not included in Table 3. This disease has occurred endemically and epidemically with different transmission patterns, which can be related to: human penetration of sylvatic foci, whether by the expansion of agricultural frontiers or other activities like eco-tourism; the rural mosaic, with the interspersing of agricultural areas with secondary forests and scrub growth; areas of urban expansion with housing projects on the limits between the city and the forest or environmental preservation areas, with the adaptation of vectors, reservoirs, and parasites to modified environments. Various factors related to the scenarios described above can be detected by images: deforested areas, by the contrast between the vegetation and the soil; new rural settlements, using the irregular texture in the deforested areas; and the opening of roads, using the information on the contrast between the vegetation and the soil and the elongated and narrow shape. In the rural pattern, the risk areas are those involving agricultural use, which are normally identified with images due to their regular shape and their interspersing with secondary forests and scrub growth, giving the appearance of a mosaic. The areas occupied by the population can be identified by the irregular pattern in the geometric shapes of the dwellings. The paths used by people to circulate, when not identified, can be inferred by the distance between rural clusters in the agricultural areas. The urban pattern is observed when, due to population growth, new housing projects are built on the limits between the city and the forest, as in Manaus, or when transmission foci are located on the limits between urbanized and environmental preservation areas, as in Rio de Janeiro. Among many factors, images acquired on different dates can identify areas of urban growth, variation in plant cover, land use, and environmental preservation areas in urban spaces. Images provided by the TM sensor in the LANDSAT satellite can provide a good option for identifying these patterns, and SPOT can be used when finer resolution is necessary.

Other endemics can also be explored, like onchocerciasis, filariasis, and dengue. The latter, in which intradomiciliary transmission is decisive in maintaining what until recently was a scarcely "visible" endemic for remote sensors, has some environmental aspects which contribute substantially to reproduction of the vector (Aedes aegypti). Open-air storage of used tires, large open water tanks, and abandoned swimming pools account for the extensive proliferation of these insects after rain and can be located using high-resolution sensors.

 

Final remarks

An environmental context predisposing to the occurrence of various endemics can be captured by the spatial, temporal, and spectral resolutions of RS satellite onboard sensors. Remote sensing, combined with other technologies like GPS (Global Positioning System), capable of spatially locating the event, and GIS (Geographic Information System), add qualified information for the identification of vulnerable ecosystems, at a relatively low cost, thus providing an important ancillary (and previously little-explored) tool for studying certain endemics and supporting surveillance and control activities.

The use of statistical and computational methods and techniques, in addition to digital processing of satellite images, expands the prospects for research on the spatial distribution of diseases and the possibility of creating risk maps based on multivariate and hierarchical models. In addition, the role of this technology remains to be explored for supporting the implementation of endemic surveillance activities. Substantial improvements can be made in estimates of vector control inputs, based on calculations of the extension of settled areas; optimization of routes for visits by health agents; and identification of potential new foci, whether by expansion of urban areas or opening of trails in the forest.

Despite the opportunities this technology offers for studying endemics, its utilization is still limited by the cost and lack of knowledge of its potential. However, some images, like those from the NOAA and TERRA satellites, can be acquired free of cost (http://daac.gsfc.nasa.gov). The CBERS 2 images are also available, free of charge, at http://www.dpi.inpe.br/catalogo, having their use restricted by the license one can find at the same address. The LANDSAT, SPOT, IKONOS images and others can be ordered for any region of Brazil via internet (INPE ­ http://www.dgi.inpe.br, GISPLAN ­ http://www.gisplan.com.br, ENGESAT ­ http://www.engesat.com.br). Some of these images, for example LANDSAT, have quite affordable prices. Although commercial software programs for data processing currently available on the market are still expensive, there is a viable public-domain alternative, SPRING­GIS, which integrates image processing functions and statistical modeling algorithms for environmental data. The greatest limitation in our opinion is technical training in the health field, allowing for the gradual incorporation of this technology.

 

Contributors

All the authors contributed to the concept, methodological development, discussion, and elaboration of the article.

 

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Correspondence to
V. R. M. Correia
Divisão de Processamento de Imagens, Instituto Nacional de Pesquisas Espaciais
Av. dos Astronautas 1758, São José dos Campos, SP 12201-027, Brasil
virginia@dpi.inpe.br  

Submitted on 15/Aug/2003
Final version resubmitted on 02/Dec/2003
Approved on 15/Dec/2003

Escola Nacional de Saúde Pública Sergio Arouca, Fundação Oswaldo Cruz Rio de Janeiro - RJ - Brazil
E-mail: cadernos@ensp.fiocruz.br