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. 2019 Oct 10;15(10):e1007369.
doi: 10.1371/journal.pcbi.1007369. eCollection 2019 Oct.

Consensus and uncertainty in the geographic range of Aedes aegypti and Aedes albopictus in the contiguous United States: Multi-model assessment and synthesis

Affiliations

Consensus and uncertainty in the geographic range of Aedes aegypti and Aedes albopictus in the contiguous United States: Multi-model assessment and synthesis

Andrew J Monaghan et al. PLoS Comput Biol. .

Abstract

Aedes (Stegomyia) aegypti (L.) and Ae. (Stegomyia) albopictus (Skuse) mosquitoes can transmit dengue, chikungunya, yellow fever, and Zika viruses. Limited surveillance has led to uncertainty regarding the geographic ranges of these vectors globally, and particularly in regions at the present-day margins of habitat suitability such as the contiguous United States. Empirical habitat suitability models based on environmental conditions can augment surveillance gaps to describe the estimated potential species ranges, but model accuracy is unclear. We identified previously published regional and global habitat suitability models for Ae. aegypti (n = 6) and Ae. albopictus (n = 8) for which adequate information was available to reproduce the models for the contiguous U.S. Using a training subset of recently updated county-level surveillance records of Ae. aegypti and Ae. albopictus and records of counties conducting surveillance, we constructed accuracy-weighted, probabilistic ensemble models from these base models. To assess accuracy and uncertainty we compared individual and ensemble model predictions of species presence or absence to both training and testing data. The ensemble models were among the most accurate and also provided calibrated probabilities of presence for each species. The quantitative probabilistic framework enabled identification of areas with high uncertainty and model bias across the U.S. where improved models or additional data could be most beneficial. The results may be of immediate utility for counties considering surveillance and control programs for Ae. aegypti and Ae. albopictus. Moreover, the assessment framework can drive future efforts to provide validated quantitative estimates to support these programs at local, national, and international scales.

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Conflict of interest statement

The authors have declared that no competing interests exist.

Figures

Fig 1
Fig 1. County-level presence or pseudo-absence of Ae. aegypti and Ae. albopictus in the contiguous U.S.
(a) Counties with presence and pseudo-absence records for Ae. aegypti and (b) with 100 km buffered pseudo-absence. (c) Ae. albopictus unbuffered and (d) buffered presence and pseudo-absence. Red dots are presence records. Dark blue "x" symbols are pseudo-absence records based on counties with known vector surveillance. Light blue "x" symbols are additional pseudo-absence records based on counties in which the other species was reported but the species in question was not.
Fig 2
Fig 2. Reproduced Ae. aegypti models.
Distribution models reproduced from (a) Christophers (1960) [54], (b) Capinha et al. (2014) [20], (c) Campbell et al. (2015) [24], (d) Kraemer et al. (2015) [25], (e) Monaghan et al. (2016) [28], and (f) Johnson et al. (2017) [30]. Red areas are predicted to be environmentally suitable for presence. Black dots are all presence records.
Fig 3
Fig 3. Reproduced Ae. albopictus models.
Distribution models reproduced from (a) Kobayashi et al. (2002) [11], (b) Medlock et al. (2006) [12], (c) ECDC (2009) [55] (d) Mogi et al. (2012) [18], (e) Campbell et al. (2015) [24], (f) Kraemer et al. (2015) [25], (g) Proestos et al. (2015) [26], and (h) Johnson et al. (2017) [30]. Red areas are predicted to be environmentally suitable for presence. Black dots are all presence records.
Fig 4
Fig 4. Model calibration.
Estimated probability of presence versus the frequency of counties reporting the species as present, by decile, for Ae. aegypti (left panels) and Ae. albopictus (right panels). The predictions are compared to both the training data (top panels) and testing data (bottom panels).
Fig 5
Fig 5. Ensemble model for Ae. aegypti.
(a) Ensemble model probability of presence; (b) ensemble model uncertainty expressed as entropy, H; (c) ensemble model in-sample residuals, E; and (d) ensemble model out-of-sample residuals, E. Black dots are presence records and black "x" marks are pseudo-absence records. All presence and absence records are shown in (a) and (b); only in-sample records are shown in (c); and only out-of-sample records are shown in (d).
Fig 6
Fig 6. Ensemble model for Ae. albopictus.
(a) Ensemble model probability of presence; (b) ensemble model uncertainty expressed as entropy, H; (c) ensemble model in-sample residuals, E; and (d) ensemble model out-of-sample residuals, E. Black dots are presence records and black "x" marks are pseudo-absence records. All presence and absence records are shown in (a) and (b); only in-sample records are shown in (c); and only out-of-sample records are shown in (d).

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