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. 2012;7(10):e46882.
doi: 10.1371/journal.pone.0046882. Epub 2012 Oct 5.

Remote sensing of climatic anomalies and West Nile virus incidence in the northern Great Plains of the United States

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Remote sensing of climatic anomalies and West Nile virus incidence in the northern Great Plains of the United States

Ting-Wu Chuang et al. PLoS One. 2012.

Abstract

The northern Great Plains (NGP) of the United States has been a hotspot of West Nile virus (WNV) incidence since 2002. Mosquito ecology and the transmission of vector-borne disease are influenced by multiple environmental factors, and climatic variability is an important driver of inter-annual variation in WNV transmission risk. This study applied multiple environmental predictors including land surface temperature (LST), the normalized difference vegetation index (NDVI) and actual evapotranspiration (ETa) derived from Moderate-Resolution Imaging Spectroradiometer (MODIS) products to establish prediction models for WNV risk in the NGP. These environmental metrics are sensitive to seasonal and inter-annual fluctuations in temperature and precipitation, and are hypothesized to influence mosquito population dynamics and WNV transmission. Non-linear generalized additive models (GAMs) were used to evaluate the influences of deviations of cumulative LST, NDVI, and ETa on inter-annual variations of WNV incidence from 2004-2010. The models were sensitive to the timing of spring green up (measured with NDVI), temperature variability in early spring and summer (measured with LST), and moisture availability from late spring through early summer (measured with ETa), highlighting seasonal changes in the influences of climatic fluctuations on WNV transmission. Predictions based on these variables indicated a low WNV risk across the NGP in 2011, which is concordant with the low case reports in this year. Environmental monitoring using remote-sensed data can contribute to surveillance of WNV risk and prediction of future WNV outbreaks in space and time.

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Conflict of interest statement

Competing Interests: The authors have declared that no competing interests exist.

Figures

Figure 1
Figure 1. Spatial empirical Bayes (SEB) smoothed WNV Incidence Rate in the Northern Great Plains throughout 2004 to 2010.
Figure 2
Figure 2. The plotting of GAM best-fitting results (a) Model Date: Jun 25 (b) Model Date: Aug 12 between WNV risk and environmental variables.
Figure 3
Figure 3. Cross-validation of generalized additive models for four model dates from 2004–2010.
The RMSE results for 2011 are a validation based on the model fitted with data from 2004–2010.
Figure 4
Figure 4. WNV relative risk forecasting maps for 2011 at the (a) model date June 25 and (b) model date July 27 and (c) 2011 SEB smoothed WNV incidence rates.
The circle indicates the Omaha-Council Bluffs metropolitan area.

References

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