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Landscape attributes influence spatial variations in disease risk or incidence. We present a review of the key findings from eight case studies that we conducted in Europe and West Africa on the impact of land changes on emerging or re-emerging vector-borne diseases and/or zoonoses. The case studies concern West Nile virus transmission in Senegal, tick-borne encephalitis incidence in Latvia, sandfly abundance in the French Pyrenees, Rift Valley Fever in the Ferlo (Senegal), West Nile Fever and the risk of malaria re-emergence in the Camargue, and rodent-borne Puumala hantavirus and Lyme borreliosis in Belgium.
We identified general principles governing landscape epidemiology in these diverse disease systems and geographic regions. We formulated ten propositions that are related to landscape attributes, spatial patterns and habitat connectivity, pathways of pathogen transmission between vectors and hosts, scale issues, land use and ownership, and human behaviour associated with transmission cycles.
A static view of the "pathogenecity" of landscapes overlays maps of the spatial distribution of vectors and their habitats, animal hosts carrying specific pathogens and their habitat, and susceptible human hosts and their land use. A more dynamic view emphasizing the spatial and temporal interactions between these agents at multiple scales is more appropriate. We also highlight the complementarity of the modelling approaches used in our case studies. Integrated analyses at the landscape scale allows a better understanding of interactions between changes in ecosystems and climate, land use and human behaviour, and the ecology of vectors and animal hosts of infectious agents.
The emergence and re-emergence of vector-borne and zoonotic diseases is controlled by ecosystem changes at the landscape level, in addition to other factors . Spatial (or landscape) epidemiology is defined as the study of spatial variation in disease risk or incidence . An integrated analysis at the landscape scale allows a better understanding of interactions between changes in ecosystems and climate, land use and human behaviour, and the ecology of vectors and animal hosts of infectious agents. Although Hippocrates already recognized the importance of the environment on health, scientists such as Jacques May and Eugene Pavlovsky formalized these ideas in the 20th century. Medical geography was defined as the study of the distribution of manifested and potential diseases over the earth's surface followed by the study of correlations between these and environmental factors . The Russian epidemiologist Pavlovsky coined the term "landscape epidemiology":
Figuratively speaking, the existence of the natural focus of a transmissible disease depends on a continuous interaction of the quintet (five) of its prerequisites associated with a specific geographic landscape .
These five prerequesites were listed as:
(1) Animal donors; (2) vectors; (3) animal recipients; (4) the pathogenic agent itself in an infective state, (5) the influence of factors of the external environments contributing to an unhindered transmission of infection from one organism to another (circulation of pathogenic agent) .
Spatial interactions between these agents in a landscape explain patterns of infection risk and may contribute to disease emergence. Analysing these complex landscape systems of interacting agents requires an interdisciplinary approach. Data from different sources and collected at different scales need to be linked, using innovative analytic methods.
As part of a broader project on the impact of environmental changes on vector-borne diseases, we conducted a series of landscape scale studies of different disease systems in Europe and West Africa. These studies allowed better understanding of the influence of landscapes on the transmission of each of these infections. Here we present a review of the key findings from these case studies on the impact of land changes on emerging or re-emerging diseases that are transmitted by arthropod vectors and/or have an animal origin (zoonoses). Through an inductive approach, we identify general principles governing spatial epidemiology, outlining a set of propositions of general validity for different diseases and geographic contexts. All these propositions are related to spatial patterns and processes associated with transmission cycles at the landscape scale. Together, they contribute to advance the theory of spatial epidemiology.
We developed various methods to understand interactions between land change, vectors, animal and human hosts. It was crucial to develop tools to link the various components of disease systems across space and to model spatial interactions. These innovations in analytic methods were a key component for developing an integrated approach of disease systems. For each site, we produced detailed land cover maps based on remote sensing data at medium to fine spatial resolutions and extracted landscape metrics. We also mapped land surface brightness, greenness, and wetness based on these data. Various spatial statistical models were used. Habitat suitability models relate the presence or abundance of vectors or animal hosts to landscape predictors that represent aspects of the species' habitat- e.g., vegetation cover, landscape configuration, surface moisture, topography, soil types. The spatial units for these models were small plots for which field observations on vector presence or abundance were collected. A variant models infection prevalence among vectors and/or hosts, as measured by field trapping in different landscapes. Another type of spatial statistical models used human cases, as compiled by public health records. Explanatory variables in these models are demographic and socio-economic variables from census data, land use maps including types of settlements, proxy variables for risk behaviours, climate and land cover. The spatial units of these latter models are administrative units at which census data are aggregated.
The Basic Reproductive Rate (R0) - which quantifies the average number of new infections that will arise from introducing an infective host into a susceptible population  - has been extensively used [6,7]. R0 is generally estimated at the aggregate level of populations. In estimating R0, the degree of contact between people and vectors is an essential factor for disease dynamics. Factors influencing people-vector contacts include the relative population densities and spatial distributions of both vectors and people , and their movements and behaviours. Previous studies based on R0 have often assumed a constant value across space of the human biting rate, given the difficulty in obtaining spatially-explicit and quantitative estimates of this variable. By coupling R0 models with spatial statistical models, we spatialized R0 and therefore better represented the spatial heterogeneity in the risk of establishment of an infection. Among the various input variables forming R0, the vector-host ratio displays the greatest spatial heterogeneity. By combining fine-scale land cover variables and coarse-scale climatic variables, we predicted the spatial distribution of vectors. This was then integrated with maps of human host distribution to spatialize the vector-host ratio in the R0 formula [8,9]. A few previous studies attempted to spatialize R0 [10-12], mostly for diseases that are transmitted directly (e.g., foot-and-mouth disease, avian influenza). These studies identified high-risk areas based on landscape data and explored characteristics of epidemics, such as the spread distance, and the efficacy of control measures. Hartemink et al.  investigated a spatial R0at district level for the veterinary blue tongue disease in the Netherlands.
We also developed a spatially-explicit modelling approach to represent spatial variations in people-vector contacts at the landscape scale using multi-agent simulations (MAS) . An agent is an autonomous computer entity capable of interacting with other agents and adapting its behaviour to a changing environment [15,16]. Agents can represent heterogeneous entities, e.g. people, animals, institutions, or land parcels, with their specific attributes and decision rules. The agent-based approach allows simulation and understanding of complex systems through the modelling of discrete events . MAS can be used as a virtual laboratory to test hypotheses impossible to test in the field. MAS are particularly well suited to model disease systems as they combine biological, environmental and social processes.
Finally, we developed a spatially-explicit population dynamics model of mosquito populations [18,19], integrating the dynamics of their breeding sites (water bodies in which the females lay their eggs), the presence of hosts, and landscape attributes controlling the spread of mosquitoes. The model is mechanistic as it uses an a priori mathematical description of the main processes determining mosquito population dynamics. It is also deterministic as it represents an average behaviour of the population an approach that is well adapted for large populations, such as mosquito populations.
The set of propositions described below were generated in an inductive manner, by generalisation from the set of empirical studies that we conducted. For each case study, we extracted the main conclusion(s) on the role of land use and land cover in the transmission cycle. The validity of these conclusions was then evaluated for each of the other case studies. In a synthesis table, we identified all the case studies for which a particular conclusion was empirically supported. We also identified disease systems for which the literature suggests that this conclusion may be valid.
We summarize below and in Table Table11 the case studies reviewed here.
Chevalier et al.  conducted a serological study on horses in five ecologically contrasted regions of the Senegal River basin (Senegal) to assess WNV transmission. Blood samples were taken from 367 horses from the five regions and screened by ELISA for anti-WNV IgM and IgG. Positive samples were then confirmed by seroneutralization. The seroprevalence rate was 85% overall but it varied significantly between sites. To assess whether environmental conditions could explain these differences, a land cover map was derived from two satellite images from the dry and wet seasons, and the surface covered by each land-cover type was calculated for each study area. Environmental data were analysed using principal components analysis and generalized linear mixed models.
Vanwambeke et al.  investigated the landscape-level factors influencing TBE incidence in rural parishes of Latvia, distinguishing between land cover, use and ownership. Land cover was used to depict the ecological suitability of the landscape for ticks and their hosts. Landscape composition and configuration were extracted from land cover maps. Land use represented human exposure to ticks, mostly through visits to forests. It was measured using proxy variables extracted from agricultural and household censuses. Land ownership of forests represented the accessibility to vector habitats for the public. Data were analysed using non-spatial and spatial negative binomial regression models.
A spatially-explicit R0 model was developed for canine leishmaniasis in the French Pyrennées . An important variable for such a model is the density of the vector, which was estimated continuously in space using multivariate regression models. Based on extensive field trapping of sandflies, and using landscape composition and configuration at a medium spatial resolution and remotely sensed climate-related factors at a coarse spatial resolution, the abundance of sandflies was predicted throughout the study area. This was then used as an input for the calculation of a spatially-explicit R0.
The impact of landscape variables on the transmission of RVF in small ruminants was investigated in the semi-arid region of Barkedji, Ferlo, Senegal . The relationship between landscape features, derived from a very high spatial resolution image, and serologic incidence was analysed statistically using a mixed-effect logistic regression model. A model of mosquito population dynamics was also developed. This model, based on current knowledge on the biology of the two RVF vectors species, Aedes vexans and Culex poicilippes, takes into account the main events of the mosquito life cycle and climatic fluctuations. Simulations of daily spatial and temporal variations in the area of temporary ponds around a village in Senegal relied on the Tropical Rainfall Measuring Mission (TRMM) rainfall product [18,19]. Mosquito population dynamics was simulated based on variations in water level and surface.
Based on the seasonal distribution of mosquito and bird populations, simulations of introduction, amplification and emergence of WNV under different realistic scenarios were produced and compared with seroprevalence measured in horse and bird populations .
The link between environmental features and PUUV prevalence in bank vole population was investigated in Belgium. Linard et al.  explored the relationship between environmental variables and host abundance, PUUV prevalence in the host, and human cases of nephropathia epidemica. Statistical analyses were carried out on 17 broadleaf forest sites. To understand causal pathways between environment and disease risk, the study distinguished between environmental factors related to the abundance of hosts, such as land-surface attributes, landscape configuration, and climate, and factors that may favour virus survival in the environment, such as climate and soil attributes. A national scale model explained the spatial distribution of PUUV human infections at the municipality level .
The impact of fine-grained landscape patterns on the exposure of people to LB infection was also investigated in Belgium. A combination of factors linked to the vector and host populations, landscape attributes, and socio-economic factors were included in a negative binomial regression to explain the number of LB cases per municipality .
A larval index for the main potential vector of malaria in the Camargue area, Anopheles hyrcanus, was defined as the probability of observing its larvae in a given site at least once over a year. It was mapped by associating in a statistical model environmental indices that were derived from high spatial resolution imagery and entomological field data (Figure (Figure1)1) . Linard et al.  developed a spatially-explicit multi-agent simulation representing the spatio-temporal dynamics of interactions between the agents that could influence malaria transmission in the Camargue: people, mosquitoes, animal hosts and landscape. This model integrates movements and behaviours of people and vectors, and factors influencing transmission risk spatially. The model allowed testing potential drivers of malaria re-emergence such as changes in biological attributes of vectors, agricultural practices, land use, tourism activities and climate. Scenarios of possible futures varied the value of exogenous variables (e.g., tourist population visiting the area), initial conditions (e.g., land cover, in response to changes in land use policies or market forces) or parameters (e.g., level of protection of visitors against mosquito bites) .
This general proposition applies to all our studies (Table (Table2).2). The distribution, density, behaviour, and population dynamics of arthropod vectors and their non-human hosts are partially controlled by landscape features. The spatial distribution of vectors and the level of transmission is thus influenced by the environment [28,29]. This was illustrated by studies testing the relationship between disease occurrence and environmental features [30,31]. The case of WNV in Senegal illustrates this link, and the subsequent propositions provide details on the causal links between landscapes and diseases (Figure (Figure2).2). In the serological study in the Senegal River basin, Chevalier et al.  found that IgG seroprevalence rate in horses was decreasing with proximity to seawater, flooded banks and salted mudflats. These landscape features acted as protective factors as they are highly unfavourable to the presence of Culex mosquitoes, the main WNV vectors. In Senegal, environmental constraints on vector distribution are more limitative for WNV transmission than bird distribution. Similar results were observed in the Camargue region, France and in Iowa, also with significant relationships between landscape features and seroprevalence of WNV [32,33], with different risk and protective factors though. This highlights the need for a landscape scale analysis of infections, especially when there are multiple possible hosts and vectors species.
Numerous studies aimed at understanding associations between land cover and disease risk focus on the presence of critical habitats for vectors or reservoir hosts [34-40]. In most cases, the surface area of those habitats was used to quantify landscape characteristics, ignoring their spatial configuration. Yet, more complex and fragmented landscapes are associated with more ecotones (i.e., transition areas between two adjacent ecosystems), which increase the likelihood of contacts between species associated with various habitats . Moreover, fragmented landscapes provide more habitats for edge species, and a greater diversity of resources. For example, ecotones between forests and open areas commonly have high tick densities , as well as higher incidence of infection . The incidence of LB was significantly associated with the importance of land cover edges between forest and herbaceous land cover types in the US [44,45]. Allan et al.  found an increasing density of infected tick nymphs with decreasing size of forest patch. In Belgium, Linard et al.  showed that the probability of LB infection was higher in areas with a large interface between settlements and forests in peri-urban areas. In the multivariate statistical analysis of TBE incidence in rural parishes of Latvia , human cases of TBE were associated with the mean area of forest patches, their shape, and the proportion of mixed and transitional vegetation cover types around forests. Conversely, TBE incidence was lower not only where there were relatively large areas of unfavourable land covers for ticks, such as arable land, but also where forests were surrounded by agricultural land. Similar results were found in the statistical model predicting the abundance of the sandfly Phlebotomus ariasi in the French Pyrenees . It was best predicted with landscape descriptors measured in a 1000-m buffer, including Shannon's landscape diversity index (i.e., a measure of the diversity and balance in landscape composition), the proportion of forests, and the mean area of forest patches. Others studies on different vector-borne and zoonotic diseases highlighted the importance of habitats configurations for infection transmission. For example, Pradier et al.  showed a significant association between WNV's level of circulation in Southern France and a landscape metrics measuring the degree of interweaving of land cover classes. Graham et al.  also demonstrated that habitat form was related to the prevalence in China of human alveolar echinococcosis caused by a helminth, the tapeworm Echinococcus multilocularis.
The proximity of vector and host habitats may not result in a high level of risk if these critical habitats are not connected spatially by landscape features favourable to the circulation of vectors and/or hosts. Spatial diffusion of vectors is particularly crucial in the case of mosquito-borne diseases. At night, when female mosquitoes generally feed, most of the hosts (e.g., humans, cattle) are immobile. The ability of female vectors to spread from their breeding sites to hosts increases host/vector contacts. Landscape features largely control these movements . The study of RVF in the semi-arid region of the Ferlo in Senegal showed that ruminant herds living around temporary water bodies were at greater risk of RVF if they were located close to ponds surrounded by vegetation . A landscape closure index - representing the proportion of surface around each pond covered by vegetation such as dense forest and shrub savannah - was positively correlated with higher serologic incidence. The presence of dense vegetation around water bodies favours the spread of mosquitoes from the pond where they breed to the nearby ruminant herds (Figure (Figure3).3). The importance of connectivity between habitats for the spread of mosquitoes was also demonstrated for Culex species in Southern France . The connectivity between forest patches may also influence rodent populations and therefore the transmission of rodent-borne diseases such as hantavirus. Linard et al.  found that the spatial distribution of bank voles was different during epidemic and non-epidemic years. The number of bank voles captured was higher in more isolated forest patches during the non-epidemic year, whereas it was higher in less isolated patches during the epidemic year. Well-connected patches have more chances to be recolonized after local extinctions . Habitat connectivity could also influence the virus occurrence in hosts by controlling movements of individuals and thus contact rate between infected and susceptible rodents. Langlois et al.  observed that hantavirus incidence in deer mice was higher in landscapes with a higher level of fragmentation of the preferred habitat. In Western Africa, Guerrini et al.  showed that the riverine forest fragmentation level is a critical factor to determine the habitat of riverine tsetse species, vectors of animal trypanosomosis.
Great numbers of hosts and vectors species are potentially involved in the transmission of WNF, making its epidemiology complex. One should better understand underlying processes accounting for observed patterns of WNF when correlations between land use/cover and disease prevalence have been established . In the Camargue region, we showed that epidemic processes of introduction, amplification and emergence of WNV were related to specific associations of hosts and vectors species in time and space. Based on maps of seasonal distributions of mosquito and bird populations, simulations of introduction, amplification and emergence of WNV were compared with seroprevalence measured in horse and bird populations . Introduction of the virus by migratory birds explained accurately the observed spatial patterns of WNV transmission, whereas overwintering of WNV in mosquitoes did not. Cx. modestus was identified as the main amplifier of WNV, which is consistent with competence studies . In the Camargue, the virus was only isolated in sparrows and magpies . Yet, other competent bird species - or all bird species - may contribute to WNV amplification. The bird community composition did not seem to play a major role in the amplification of WNV in the Camargue (no "dilution effect"), unlike what was observed in the New World [52,55,56]. The final risk map, based on landscape attributes, synthesizes the different processes leading to WNV emergence in horses and identifies risk areas requiring veterinary surveillance.
The transmission of vector-borne diseases requires a direct contact - i.e., a bite - between an infectious vector and a susceptible host. By contrast, zoonoses such as PUUV can be transmitted directly, by physical contact between infected and susceptible hosts, or indirectly, with the environment as an intermediate. Actually, the virus can be shed in the environment via rodent excretions, and transmitted to humans in aerosols [57,58]. The environmental conditions controlling the direct and indirect transmission paths differ. In a study of the link between environment and PUUV prevalence in bank voles in Belgium, Linard et al.  showed that PUUV prevalence among bank voles is more linked to variables favouring the survival of the virus in the environment, and thus indirect transmission. In particular, low winter temperatures were strongly linked to high prevalence among bank voles, and high soil moisture was associated with high numbers of nephropathia epidemica cases among humans. The risk of transmission to humans is therefore not only determined by host abundance, but also by the indirect transmission path, largely controlled by climatic factors and soil characteristics influencing virus survival in the environment. Another illustration is provided by the differences in dynamics of two pathogens vectored by the same species, Borrelia spp. and TBE virus. Transmission to ticks related to systemic and non-systemic host infections (respectively, infection of many and specific parts of the body) has been described for both pathogens. Yet, transmission through co-feeding of ticks in non-systemically infected hosts may be more important to sustain the transmission of TBE [59,60]. As a result, spatial variations of TBE infection risk are controlled by more restrictive ecological conditions, as closer interactions between infected competent hosts and ticks are required compared to LB. The TBE transmission cycle is therefore more fragile [61,62]. The transmission via the environment can also play a role in the transmission of avian influenza viruses: contaminated water supplies can constitute a reservoir that maintains the virus in the environment and be a source of contamination for wild or domestic birds .
The emergence of a disease in a particular region is associated with multiple macro-level changes such as a shift in political and economic regimes that influence people's livelihood strategies and therefore their interaction with natural ecosystems [64,65], rapid conversion of natural habitats, and urbanization. In some cases, variations in climate may act synergistically with these socio-economic changes, even though the relative magnitude of climate change impacts remains contentious . Macro-economic and climatic conditions create favourable or unfavourable background conditions for the development of pathogens, vectors, and hosts. The actual realisation of the transmission cycle and transmission to humans depends on the overlap of the preferred habitats of competent vectors and infected hosts, and on the entry of humans into these infected areas. Therefore, the fine-grained spatial heterogeneity in disease emergence is determined by natural and cultural landscape attributes that act as fine-scale spatial determinants of the multiple factors controlling the transmission cycle. For example, while an acceleration of warming of spring temperatures in the Baltic region played some role in the dramatic increase in TBE incidence , it did not account for the high spatial heterogeneity of incidence at an infra-national scale. Landscape factors related to the ecology of the disease and to human activities better explain this spatial heterogeneity . In Western Europe, bank voles are known to display cyclic abundance peaks, which significantly increase PUUV infection among rodents and humans. These peaks are related to high tree seed production, triggered by high summer and autumn temperatures the preceding years [68,69]. While such macro-scale factors influence PUUV incidence at the regional scale, landscape characteristics related to rodent habitats and human land use determine the local scale spatial heterogeneity of transmission. Spatial variations in sandfly abundance in the French Pyrenees was also explained by a combination of coarse and fine resolution remotely-sensed metrics that are associated with, respectively, regional climatic trends and local-scale landscape variables reflecting land use . In (disease) ecology, the relevance of the scale factor has been widely demonstrated  and yet it remains poorly explored in empirical studies of landscape epidemiology.
In the semi-arid region of the Ferlo, Senegal, temporary ponds - i.e., that are flooded after the first rains and remain dry for most of the dry season - constitute a favourable habitat for RVF vectors, Ae. vexans and Cx. poicilippes. Modelling spatial and temporal variations in water level and surface of temporary ponds around a village in Senegal allowed simulating mosquito population dynamics and host distribution [18,19]. Results showed that rainfall drives Culex and Aedes populations and therefore the risk of circulation of RVF virus. Depending on the frequency of rainfall events, high densities of Culex and Aedes may occur simultaneously. This co-occurrence of species leads to a higher risk of transmission, Ae. vexans and Cx. poicilipes acting as, respectively, initiators and amplifiers of RVF virus circulation. Thus, in the Ferlo region, a combination of rainfall frequency and amount identifies years at risk for RVF. Landscape features also influence the spread distance of mosquitoes away from their breeding sites . In East Africa, heavy rainfall events were associated with RVF outbreaks . Such events lead to major increase in mosquito vector populations . The flooded areas that are potential mosquito breeding sites ("dambos") constitute the main risk areas . Meteorological conditions can also influence exposure of humans .
Land cover is defined by the attributes of the earth's land surface and immediate subsurface, including biota, soil, topography, surface and groundwater, and human structures. Land use is defined by the purposes for which humans exploit the land cover. While a focus on land cover helps understanding the presence of vectors and hosts, a focus on land use identifies which places people visit for specific activities, at what time of the day and of the year, and at what frequency. The attractivity of various places for a given activity depends on their attributes such as accessibility and value for that activity - e.g., presence of recreational features, easily accessible forests with amenities such as good trails. Our studies on human cases of PUUV and LB in Belgium showed that the spatial distributions of the two diseases were very dissimilar . PUUV was mostly prevalent in forested, rural and low income municipalities as transmission to humans was mostly associated with hunting and forestry work. By contrast, LB was mostly found in forested, peri-urban and wealthy municipalities, as infection was mostly associated with gardening and recreational activities in forests. Thus, it is less land cover (i.e., the presence of broad-leaved forests) than land use (associated with income level and type of settlements) that controls the spatial distribution of human cases of these two diseases. Agents involved in different land uses - e.g., a tourist and a local farmer - also have varying levels of awareness of the risk of infection transmission and rate of adoption of preventive measures. Socio-economic factors such as income and education have been quantitatively related to frequency of human visits to forests and exposure to tick bites . In Latvia, the main reasons for people to enter forests included looking for alternative livelihood sources or recreation. People with low income and education visit forests more commonly with the purpose of collecting wild food, while more wealthy and educated people are more likely to visit forests for recreation . In our study of TBE incidence in rural parishes of Latvia , human cases of TBE were positively related to variables indicating wild food pickers and negatively related to variables associated with hikers. Different socio-economic groups are represented in various proportions in different regions of a country. In the Camargue, the scenarios tested using a multi-agent simulation showed that water management practices in rice fields influence the rate of contact between people and potential malaria vectors . According to the flooding date of rice fields, the maximum abundance of vectors and people can be reached simultaneously, resulting in high contact rates. In a study on West Nile Virus disease risk in the US, Winters et al.  emphasized the importance of taking into account human activities to assess risk of vector exposure in montane areas heavily used for recreation in the summer.
Land ownership and access rules determine whether distributions of ticks and human activities overlap in space and time. In most countries, State forests are more accessible to the public than privately-owned forests. In the statistical analysis of TBE incidence in rural parishes of Latvia , land ownership proved to be an important explanatory variable, with a positive relationship between TBE incidence and the presence of State-owned forests. Because forest ownership is associated with different forest management practices, land ownership may reflect not just access to forests but also differences in forest management practices. The latter have an impact on habitat quality for ticks and tick-hosts, and on the attractiveness of forests for human activities. For example, forest age, use of plantation and sanitary cutting may affect the presence of ticks, rodents, and forest food. While issues of land ownership have been widely studied in conservation science , they have been ignored in landscape epidemiology.
Humans can adopt a range of preventive measures to decrease the risk of contact with vectors or pathogens. The rate of adoption of these measures depends on the availability of such preventive measures, the nuisance of the vector, the risk of infection and its level of perception by susceptible agents. For transmission to occur, one needs a combination of a conducive environment, which is created by an ecosystem favourable to interactions between pathogens, vectors and their animal hosts, and risk behaviours by human hosts that lead to a greater incidence among a human population. For example, the emergence of TBE in the Baltics was associated with a complex combination of abiotic, biotic and human factors [64,75]. Similarly, the spatial distributions of PUUV and LB infections in Belgium were related to human activities and behaviours, among other factors . In an area of Sweden endemic for TBE and LB, differences were found in adoption of preventive measures between permanent and part-time residents and between genders, suggesting differing risk perception . Dengue infection in northern Thailand was explained by variables related to the ecology of Aedes, the mosquito vector, and by risk and protective behaviours [79,80]. One of the greatest challenges in landscape epidemiology is to better integrate human behaviours.
The above propositions have the status of hypotheses requiring further testing in different geographic and biological contexts. Yet, they further our understanding of the impact of land-use and land-cover change on the transmission cycle of vector-borne diseases. A practical implication of this enhanced knowledge is to identify indicators of "pathogenic landscapes", to provide early warning signals of an increased likelihood of disease transmission. A static view of the "pathogenicity" of landscapes overlays maps of the spatial distribution of: (i) vectors and their habitats, (ii) animal hosts carrying specific pathogens and their habitat, (iii) susceptible human hosts and their land use. A more dynamic view would represent the spatial and temporal dynamics of these agents at multiple scales. Potential indicators of a higher transmission risks would be derived from any combination of social and ecological processes that are associated with spatial boundaries and temporal transitions that increase - or create new - interactions between disease transmission agents. Spatial indicators of infection risks would be associated with ecotones; margins of the geographic distributions of vectors, hosts or pathogens; and highly connected places, being at the crossroad of circulating vectors, hosts or pathogens. Temporal indicators of infection risks would be associated with biological mutation of pathogens, invasion of vectors, change in composition of animal host population, migration of naïve human hosts, abrupt land use/cover changes (not just land cover conversions but also subtle land cover modifications), political and economic changes, rapid climatic changes... Importantly, it is synergistic interactions between several of these indicators that are most likely to be associated with high infection risks.
The above findings have implications for the design of public health surveillance systems. For example, georeferencing of serological data collected on hosts is essential. For human cases, recording the place of infection in addition to the place of residence of patients is also necessary. Systematic trapping of vectors and/or animal hosts for serological surveys should be spatially targeted on areas with a high risk of transmission. This could be achieved through spatially stratified sampling schemes defined based on the relevant landscape attributes. Budgeting should allow for rapidly increasing the intensity of serological surveys on hosts in periods of unexpected socio-economic, ecological or climatic transitions that have the potential to affect transmission of infections. Data on land cover, land use, and socio-economic factors associated with risk behaviours should be systematically integrated in surveillance systems. Finally, the ability of public health analysts to integrate data from different sources, at multiple scales, and representing various components of disease systems should be enhanced.
The different modelling approaches used in the case studies were highly complementary. A detailed and accurate land cover mapping by remote sensing was at the basis of the methods used. Spatial statistical models were used to explore empirical relationships between disease systems and landscape patterns, as a preliminary approach of disease systems for the development of more integrated models. The finding of statistically significant associations does not establish causal relationships. Moreover, regression models cannot be used for extrapolation beyond the region of the variable space corresponding to the original data. R0 models allow investigation of establishment potential in the absence of a disease. They are based on a representation of biological processes of transmission. Yet, the spatial heterogeneity of environmental attributes is not explicitly included in these models. The development of multi-agent simulations necessitates a considerable amount of data and a good preliminary knowledge of the disease system. MAS represent the dynamics of people-vector contacts in space and time and are therefore ideal to explore scenarios associated with conditions that have not been observed previously. Coupling R0 models with MAS could therefore better represent the influence of spatial and temporal heterogeneity in people-vector contacts on the risk of establishment of an infection. There is a logical sequence in the use of the various methods, from the land cover description by remote sensing to the spatially-explicit multi-agent simulation, transiting through exploratory statistical analyses to better understand the key components of disease transmission and their associations.
We conclude as we started, with a quote by E.N. Pavlovsky (1966):
"The epidemiological significance of a locality is determined by the following factors: (a) the landscape of an area with natural foci of diseases in newly-settled and reclaimed regions (...); (b) the extent and nature of contact between man and his natural environment."
All our case studies show that spatial variations in infection risk are controlled by three sets of factors: (i) the pathogenic cycle and the biology of vectors, hosts and pathogens; (ii) ecosystem processes at the landscape scale, as influenced by ecosystem structure and composition, landscape connectivity and configuration, climate, species interactions; and (iii) land use, human behaviour and mobility, knowledge and perception of disease risk, and socio-economic conditions. In general, previous studies in spatial epidemiology have ignored or given less emphasis to the latter set of factors (i.e., land use and human behaviours). The challenge in landscape epidemiology is to integrate dynamically these different factors, with an emphasis on their interactions and not just on their spatial overlay. By identifying a set of propositions on factors controlling these interactions, this review contributes to a general understanding of spatial variations in disease risk.
The authors declare that they have no competing interests.
EFL designed and coordinated the synthesis study. AT, SV, CL, VS contributed to the synthesis study and analyzed the data for individual case studies. All authors wrote, read and approved the final manuscript.
This study was funded by EU Grant GOCE-2003-010284 EDEN; it has been catalogued by the EDEN Steering Committee as EDEN247 http://www.eden-fp6project.net. We are grateful to partners of the EDEN project who have shared their data and expertise on the case studies.