Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2021 Feb 10;288(1944):20202810.
doi: 10.1098/rspb.2020.2810. Epub 2021 Feb 3.

Dispersal in heterogeneous environments drives population dynamics and control of tsetse flies

Affiliations

Dispersal in heterogeneous environments drives population dynamics and control of tsetse flies

Hélène Cecilia et al. Proc Biol Sci. .

Abstract

Spatio-temporally heterogeneous environments may lead to unexpected population dynamics. Knowledge is needed on local properties favouring population resilience at large scale. For pathogen vectors, such as tsetse flies transmitting human and animal African trypanosomosis, this is crucial to target management strategies. We developed a mechanistic spatio-temporal model of the age-structured population dynamics of tsetse flies, parametrized with field and laboratory data. It accounts for density- and temperature-dependence. The studied environment is heterogeneous, fragmented and dispersal is suitability-driven. We confirmed that temperature and adult mortality have a strong impact on tsetse populations. When homogeneously increasing adult mortality, control was less effective and induced faster population recovery in the coldest and temperature-stable locations, creating refuges. To optimally select locations to control, we assessed the potential impact of treating them and their contribution to the whole population. This heterogeneous control induced a similar population decrease, with more dispersed individuals. Control efficacy was no longer related to temperature. Dispersal was responsible for refuges at the interface between controlled and uncontrolled zones, where resurgence after control was very high. The early identification of refuges, which could jeopardize control efforts, is crucial. We recommend baseline data collection to characterize the ecosystem before implementing any measures.

Keywords: disease vector; experimental and field data; mechanistic modelling; mortality scenario; spatio-temporal dynamics.

PubMed Disclaimer

Conflict of interest statement

We declare we have no competing interests.

Figures

Figure 1.
Figure 1.
Within-cell model diagram of tsetse fly population dynamics (time unit: day). Transitions between stages except from pupa (P) to nulliparous female (N) trigger the birth of a new pupa P1. Transitions occur at development rate δS for stage S ∈ {P, N, Fx} (parity x ∈ {1, 2, 3, 4+}) according to temperature θt,c at time t in cell c, giving rise daily to a minimum jump of l states from each state i of stage S, with (1−q)St,c,i individuals going from state St,c,i to state St+1,c,i+l and qSt,c,i individuals going to St+1,c,i+l+1. If i + l > nS (respectively, i + l + l > nS, with nS the maximum number of states in stage S ∈ {P, N, Fx}), then selected individuals go to the next stage. Equations are in the electronic supplementary material, S4.1. (Online version in colour.)
Figure 2.
Figure 2.
Mortality increase and tsetse fly population size. (a) Relative increase in mortality needed to reduce the female population size to 2% (circle) or 5% (triangle) of its initial size after 1 year of control, when a fraction of cells was targeted. (b) Contribution of cells to the total population size ((i): no control, (ii): homogeneous control, (iii): heterogeneous control targeting 47% of the cells). (c) Local control efficacy ((i)–(ii): same as in b), the darkest being the most effective (lighter colour: uncontrolled cells). (Online version in colour.)
Figure 3.
Figure 3.
Local population resurgence 1 year after the end of a homogeneous control. (a) Local growth rate, (bd) variations of the local growth rate with carrying capacity, mean annual temperature and annual standard deviation of temperature. Colours: control efficacy (blue (bottom colour): most effective). (Online version in colour.)
Figure 4.
Figure 4.
Local population resurgence 1 year after the end of a heterogeneous control (47% of controlled cells). (a) Local growth rate, (bd) variations of the local growth rate with carrying capacity, mean annual temperature and annual standard deviation of temperature. Colours: control score (the highest: still targeted when the proportion of controlled cells is reduced). Cyan: uncontrolled cells. (Online version in colour.)

References

    1. Vinatier F, Tixier P, Duyck PF, Lescourret F. 2011. Factors and mechanisms explaining spatial heterogeneity: a review of methods for insect populations. Methods Ecol. Evol. 2, 11–22. (10.1111/j.2041-210X.2010.00059.x) - DOI
    1. Pulliam HR 1988. Sources, sinks and population regulation. Am. Nat. 132, 652–661. (10.1086/284880) - DOI
    1. Keppel G, Anderson S, Williams C, Kleindorfer S, O'Connell C. 2017. Microhabitats and canopy cover moderate high summer temperatures in a fragmented Mediterranean landscape. PLoS ONE 12, e0183106 (10.1371/journal.pone.0183106) - DOI - PMC - PubMed
    1. Clark JS 2005. Why environmental scientists are becoming Bayesians. Ecol. Lett. 8, 2–14. (10.1111/j.1461-0248.2004.00702.x) - DOI
    1. Crone E 2016. Contrasting effects of spatial heterogeneity and environmental stochasticity on population dynamics of a perennial wildflower. J. Ecol. 104, 281–291. (10.1111/1365-2745.12500) - DOI

Publication types

LinkOut - more resources