Bluetongue Disease Risk Assessment Based on Observed and Projected Culicoides obsoletus spp. Vector Densities
Rubel F (2013) Bluetongue Disease Risk Assessment Based on Observed and Projected Culicoides obsoletus spp. Vector Densities. PLoS
ONE 8(4): e60330. doi:10.1371/journal.pone.0060330
Bluetongue Disease Risk Assessment Based on Observed and Projected Culicoides obsoletus spp. Vector Densities
Katharina Brugger 0
Franz Rubel 0
Simon Gubbins, Institute for Animal Health, United Kingdom
0 Institute for Veterinary Public Health, University of Veterinary Medicine Vienna , Vienna , Austria
Bluetongue is an arboviral disease of ruminants causing significant economic losses. Our risk assessment is based on the epidemiological key parameter, the basic reproduction number. It is defined as the number of secondary cases caused by one primary case in a fully susceptible host population, in which values greater than one indicate the possibility, i.e., the risk, for a major disease outbreak. In the course of the Bluetongue virus serotype 8 (BTV-8) outbreak in Europe in 2006 we developed such a risk assessment for the University of Veterinary Medicine Vienna, Austria. Basic reproduction numbers were calculated using a well-known formula for vector-borne diseases considering the population densities of hosts (cattle and small ruminants) and vectors (biting midges of the Culicoides obsoletus spp.) as well as temperature dependent rates. The latter comprise the biting and mortality rate of midges as well as the reciprocal of the extrinsic incubation period. Most important, but generally unknown, is the spatio-temporal distribution of the vector density. Therefore, we established a continuously operating daily monitoring to quantify the seasonal cycle of the vector population by a statistical model. We used cross-correlation maps and Poisson regression to describe vector densities by environmental temperature and precipitation. Our results comprise time series of observed and simulated Culicoides obsoletus spp. counts as well as basic reproduction numbers for the period 2009-2011. For a spatio-temporal risk assessment we projected our results from the location of Vienna to the entire region of Austria. We compiled both daily maps of vector densities and the basic reproduction numbers, respectively. Basic reproduction numbers above one were generally found between June and August except in the mountainous regions of the Alps. The highest values coincide with the locations of confirmed BTV cases.
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Funding: The research was supported by the PL2 Start-up project bluetongue disease model of the University of Veterinary Medicine Vienna. The funders had no
role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing Interests: The authors have declared that no competing interests exist.
Veterinary authorities are generally interested in a
spatiotemporal risk assessment to establish efficient protection and
control measures when facing diseases with high economic impact
such as caused by the Bluetongue virus (BTV). Such risk
assessments are frequently based on one common epidemiological
parameter, the basic reproduction number R0. It describes the
number of secondary cases caused by a primary case in a
completely susceptible population at the beginning of an epidemic.
Thus, R0 may be interpreted as a threshold parameter: a major
disease outbreak may only occur for R0w1, while for R0v1 the
disease will fade out [1].
The motivation for this study was the Bluetongue virus serotype
8 (BTV-8) epidemics in Europe, which emerged in 2006 at the
border triangle of Belgium, Germany and the Netherlands [2,3].
Within a few years this arboviral disease rapidly spread across
North-western and Central Europe [4,5] and caused substantial
losses in agriculture amounting to millions Euro [6]. Beside
movement restrictions and surveillance, the main veterinary
measure was to vaccinate the susceptible populations beginning
in 2008 [7]. In Austria, only a few cattle near the border to
Germany were confirmed to be BTV-8 seropositive. Due to the
German vaccination campaigns achieving a coverage of 78% [8]
and preventive vaccination in Austria the eastwards spread of the
Bluetongue disease could be stopped at the German-Austrian
border (Figure 1).
In the course of the European BTV-8 outbreak several methods
for the calculation of R0 have been proposed. Some of these
methods are based on data from surveillance and monitoring
programmes. For example, [9] estimated R0 between herds for the
Netherlands. Furthermore, a theoretical study on R0 using a
deterministic epidemic model was introduced by [10] to
investigate the seasonal spread of BTV over several years and to evaluate
the effectiveness of vaccination strategies. Most approaches
presented so far considered temperature dependent vector
parameters as well as host and vector densities. While [11]
presented a general concept on the calculation of R0 for which
they discussed the influence of temperature on the transmission
cycle, [12] and [13] generated spatial R0 maps for the Netherlands
and Switzerland, respectively. Furthermore, the uncertainty and
sensitivity of such temperature-dependent models have been
analysed and temperature turned out to be the most dominant
factor for determining the magnitude of R0 [14]. [15] estimated
the possible impact of past and future climates on the basic
reproduction number R0 on an European scale. For their study
they used input data from climate model runs applied to different
emission scenarios of the Intergovernmental Panel on Climate
Change (IPCC). The authors have used a similar approach for
modelling another mosquito-borne disease outbreak, the Usutu
virus epidemics in Vienna [16]. Here we present a predictive risk
assessment method based on the basic reproduction number R0
after [12] applied to a potential Bluetongue outbreak in Austria.
Results comprise regions at risk on a spatio-temporal scale
representative for a resolution of 10 km and 1 day.
In general, BTV circulates in a natural transmission cycle
between vectors (Culicoides biting midges) and hosts (ruminants:
mainly cattle, sheep, and goats). For risk assessment using the
concept of R0 the knowledge of both the vector and the host
densities are of fundamental importance. While the population
densities of farm animals are well documented in national
veterinary databases or available worldwide on a regular grid
[17], the vector density is generally not well known or rather
unknown. Therefore, a central part of our study is concerned with
the estimation of the vector population. We established a
continuously operating daily Culicoides spp. monitoring at the
University of Veterinary Medicine Vienna, Austria, to quantify the
seasonal abundance for at least three years. This approach is in
contrast to former - mainly weekly - monitoring programs, such as
the large-scale entomological surveillance program throughout the
European Union to investigate the occurrence and geographical
distribution of Culicoides (...truncated)