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. 2020 Dec 2;225(6):1050–1061. doi: 10.1093/infdis/jiaa746

Table 2.

Effect of Annual Molluscicide Application in Terms of Mean Worm Burden (MWB) Reduction in the Human Host Population

Seasonality Molluscicide EfficacyεS ,% Time Points Within the Seasonal Cycle for Molluscicide Application τ
0 1/10 1/4 1/2 3/4 9/10
Type I
Strong seasonality amplitude a=0.9 50 13.5 13.3 8.0 3.8 8.4 11.9
70 20.3 19.4 11.9 5.7 13.5 18.3
90 30.7 28.2 17.1 10.6 23.8 29.4
Moderate seasonality amplitude a=0.5 50 8.8 8.7 7.5 4.8 6.4 8.1
70 13.7 13.6 11.3 7.8 10.3 12.8
90 22.0 21.1 17.0 12.3 17.8 21.2
Type II
Strong seasonality amplitude a=0.6 50 19.2 18.0 9.2 6.5 13.2 17.2
70 27.0 24.9 12.8 8.5 19.6 24.8
90 38.0 33.9 17.6 14.2 32.0 37.1
Moderate seasonality amplitude a=0.3 50 9.3 9.2 7.7 4.5 6.4 8.4
70 14.5 14.3 11.5 7.0 10.4 13.4
90 23.1 22.1 17.2 11.6 18.3 22.2

Data are percent reduction in MWB.

A 6-year control program was simulated using a Macdonald-type model system having a dynamic snail population seasonality with carrying capacity function K(t,a) of trigonometric type I or peak type II structure. As for Table 1, progress was measured by relative seasonal average reduction of MWB w¯(Y6,τ)/w¯(Y0,τ). We examined several possible intraseasonal timings for molluscicide application,τ={0,110,14,12,34,910}, as fractions of the seasonal cycle, 3 possible levels of molluscicide efficacy (percent of killed snails) εS={50%,70%,90%}, and 2 choices of the seasonal amplitude parameter (moderate or high). Optimal timing for molluscicide control in all cases was τ=0 (highlighted in bold), ie, at the start/end of the season, when the snail population or its carrying capacity reached its maximum.