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. 2019 May;4(5):854-863.
doi: 10.1038/s41564-019-0376-y. Epub 2019 Mar 4.

Past and future spread of the arbovirus vectors Aedes aegypti and Aedes albopictus

Affiliations

Past and future spread of the arbovirus vectors Aedes aegypti and Aedes albopictus

Moritz U G Kraemer et al. Nat Microbiol. 2019 May.

Erratum in

  • Publisher Correction: Past and future spread of the arbovirus vectors Aedes aegypti and Aedes albopictus.
    Kraemer MUG, Reiner RC Jr, Brady OJ, Messina JP, Gilbert M, Pigott DM, Yi D, Johnson K, Earl L, Marczak LB, Shirude S, Weaver ND, Bisanzio D, Perkins TA, Lai S, Lu X, Jones P, Coelho GE, Carvalho RG, Van Bortel W, Marsboom C, Hendrickx G, Schaffner F, Moore CG, Nax HH, Bengtsson L, Wetter E, Tatem AJ, Brownstein JS, Smith DL, Lambrechts L, Cauchemez S, Linard C, Faria NR, Pybus OG, Scott TW, Liu Q, Yu H, Wint GRW, Hay SI, Golding N. Kraemer MUG, et al. Nat Microbiol. 2019 May;4(5):900. doi: 10.1038/s41564-019-0429-2. Nat Microbiol. 2019. PMID: 30903094 Free PMC article.
  • Publisher Correction: Past and future spread of the arbovirus vectors Aedes aegypti and Aedes albopictus.
    Kraemer MUG, Reiner RC Jr, Brady OJ, Messina JP, Gilbert M, Pigott DM, Yi D, Johnson K, Earl L, Marczak LB, Shirude S, Weaver ND, Bisanzio D, Perkins TA, Lai S, Lu X, Jones P, Coelho GE, Carvalho RG, Van Bortel W, Marsboom C, Hendrickx G, Schaffner F, Moore CG, Nax HH, Bengtsson L, Wetter E, Tatem AJ, Brownstein JS, Smith DL, Lambrechts L, Cauchemez S, Linard C, Faria NR, Pybus OG, Scott TW, Liu Q, Yu H, Wint GRW, Hay SI, Golding N. Kraemer MUG, et al. Nat Microbiol. 2019 May;4(5):901. doi: 10.1038/s41564-019-0440-7. Nat Microbiol. 2019. PMID: 30962571 Free PMC article.

Abstract

The global population at risk from mosquito-borne diseases-including dengue, yellow fever, chikungunya and Zika-is expanding in concert with changes in the distribution of two key vectors: Aedes aegypti and Aedes albopictus. The distribution of these species is largely driven by both human movement and the presence of suitable climate. Using statistical mapping techniques, we show that human movement patterns explain the spread of both species in Europe and the United States following their introduction. We find that the spread of Ae. aegypti is characterized by long distance importations, while Ae. albopictus has expanded more along the fringes of its distribution. We describe these processes and predict the future distributions of both species in response to accelerating urbanization, connectivity and climate change. Global surveillance and control efforts that aim to mitigate the spread of chikungunya, dengue, yellow fever and Zika viruses must consider the so far unabated spread of these mosquitos. Our maps and predictions offer an opportunity to strategically target surveillance and control programmes and thereby augment efforts to reduce arbovirus burden in human populations globally.

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Conflict of interest statement

The authors declare no competing interests.

Figures

Fig. 1
Fig. 1. Reconstruction of Ae. albopictus and Ae. aegypti spread.
ac, Spread of Ae. albopictus (a) and Ae. aegypti (b) in the United States, and spread of Ae. albopictus in Europe (c). Estimates of speed of spread in km per year are based on thin spline regression on mosquito observations since their earliest detection in each continent. Red indicates fast dispersal whereas yellow and white indicate slower spread velocity measured in km per year (see legend below b). Areas highlighted in grey have no reported mosquito presence. df, Summaries of the speed of dispersal of Ae. albopictus (d) and Ae. aegypti (e) spread in the United States and of Ae. albopictus spread in Europe (f) starting from their date of first detection until 2017. The red line indicates the average velocity per year across all districts using the thin spline regression model.
Fig. 2
Fig. 2. Predicted future spread of Ae. aegypti and Ae. albopictus in the United States.
Spread was estimated using human-mobility metrics and ecological determinants fitted to past occurrence data. a, Forecasted change in the distribution of Ae. aegypti between 2020 and 2050 using the medium climatic scenario RCP 6.0 at the US county-level ranging from −0.25 (blue) to 0.25 (red). Red indicates expansion and dark blue contraction of the Aedes range distribution between 2020 and 2050. b, The predicted habitat suitability for the presence of Ae. aegypti in 2050. Pixels with no predicted suitability are in grey. c,d, The corresponding results of a and b for Ae. albopictus.
Fig. 3
Fig. 3. Predicted future spread of Ae. albopictus in Europe.
a, The expansion (red) and contraction (blue) of Ae. albopictus between 2020 and 2050 under the medium climate scenario RCP 6.0, with emissions peaking in 2080. b, The predicted distribution of Ae. albopictus and predicted habitat suitability for the presence of Ae. albopictus in 2050. Pixels with no predicted suitability are in grey.
Fig. 4
Fig. 4. Predicted global geographical distribution of Ae. aegypti and Ae. albopictus.
ad, The distribution of Ae. aegypti (a) and Ae. albopictus (b) in 2050 under the medium climatic scenario RCP 6.0 and uncertainty for Ae. aegypti (c) and Ae. albopictus (d). Predicted habitat suitability of Ae. aegypti quantile cut-off points were 0.24, 0.66, 0.88. Relative uncertainty was computed as the ratio of the 95% uncertainty intervals and predicted Ae. aegypti suitability for each pixel. Cut-off points for uncertainty were 0.08, 0.18, 0.31. The lowest quantile of predicted suitability is shown in white and the highest in dark pink. The lowest quantile for uncertainty is white and the highest is blue. The colours overlap such that areas in purple have both high predicted suitability of Ae. aegypti and high relative uncertainty. Pixels with high predicted suitability are shown in red whereas pixels with no predicted suitability are in grey. Predicted habitat suitability of Ae. albopictus quantile cut-off points were 0.13, 0.41, 0.70. Cut-off points for uncertainty for Ae. albopictus were 0.16, 0.36, 0.53. e,f, The global population predicted to live in areas suitable for Ae. aegypti (e) and Ae. albopictus (f) under the conservative (RCP 4.5), medium (RCP 6.0) and worst-case scenario (RCP 8.5) using the binary cut-off values of suitability of 0.46 and 0.51 for both species, respectively.

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