Hargrove J W
Bull Entomol Res. 2005 Feb;95(1):13-21. doi: 10.1079/ber2004335.
A stochastic branching process was used to derive equations for the mean and variance of the probability of, and time to, extinction in tsetse populations. If the remnant population is a single inseminated female, the extinction probability increases linearly with adult mortality and is always certain if this mortality >3.5% per day even for zero pupal mortality. If the latter mortality is 4% per day, certain extinction is only avoided if adult mortality <1.5% per day. For remnant female populations >1, the extinction probability increases in a non-linear manner with adult mortality. Extinction is still certain for adult mortality >3.5% per day but, when the remnant population is >16, extinction is highly unlikely for adult mortality <2.5% per day if all females are inseminated. Extinction probability increases with increasing probability of sterile mating in much the same way as it does with increasing adult mortality. Extinction is assured if the probability of insemination can be reduced to 0.1. The required reduction decreases with increasing adult mortality. For adult mortality = 6-8% per day, the time to extinction increases only by one generation per order of magnitude increase in the starting population. Time to extinction is less sensitive to changes in the pupal than in the adult mortality. Reductions in the probability of insemination only become important when adult mortality is small; if the adult mortality is 8% per day, reducing the insemination probability from 1 to 0.1 only reduces the expected time to extinction by two generations. Conversely, increases in adult mortality produce important reductions in the required time even when the probability of insemination is 0.1. The practical, economic implication for the sterile insect technique is that the low-tech methods used to suppress tsetse populations should not be halted when the release of sterile males is initiated. The sterile insect technique should only be contemplated when it has been demonstrated that the low-tech methods have failed to effect eradication. The theory is shown to be in good accord with the observed results of tsetse control campaigns involving the use of odour-baited targets in Zimbabwe and the sterile insect technique on Unguja Island, Zanzibar.
采用随机分支过程推导采采蝇种群灭绝概率及灭绝时间的均值和方差方程。如果残余种群是一只受精雌蝇,灭绝概率随成虫死亡率呈线性增加,并且即使蛹死亡率为零,若成虫死亡率>3.5%/天,灭绝也总是必然的。如果蛹死亡率为4%/天,只有当成虫死亡率<1.5%/天时才能避免必然灭绝。对于大于1的残余雌蝇种群,灭绝概率随成虫死亡率呈非线性增加。成虫死亡率>3.5%/天时灭绝仍然是必然的,但是,当残余种群>16时,如果所有雌蝇都已受精,成虫死亡率<2.5%/天时灭绝极不可能。灭绝概率随不育交配概率增加而增加,其方式与随成虫死亡率增加大致相同。如果受精概率能降至0.1,则必然灭绝。所需降低幅度随成虫死亡率增加而减小。对于成虫死亡率=6 - 8%/天,灭绝时间每增加一个数量级的起始种群仅增加一代。灭绝时间对蛹死亡率变化的敏感性低于对成虫死亡率变化的敏感性。只有当成虫死亡率较低时,受精概率的降低才变得重要;如果成虫死亡率为8%/天,将受精概率从1降至0.1只会使预期灭绝时间减少两代。相反,如果受精概率为0.1,成虫死亡率的增加会使所需时间大幅减少。不育昆虫技术的实际经济意义在于,当开始释放不育雄蝇时,用于抑制采采蝇种群的低技术方法不应停止。只有在已证明低技术方法未能实现根除时,才应考虑采用不育昆虫技术。该理论与在津巴布韦使用诱蝇目标以及在桑给巴尔岛温古贾岛使用不育昆虫技术的采采蝇控制活动的观察结果高度一致。