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BIOLOGICAL CONTROL IN A DISTURBED ENVIRONMENT

机译:扰动环境中的生物控制

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Most ecological and epidemiological models describe systems with continuous uninterrupted?ted interactions between populations. Many systems, though, have ecological disturbances, such as those associated with planting and harvesting of a seasonal crop. In this paper, we introduce host-parasite-hyperparasite systems as models of biological control in a disturbed environment, where the host-parasite interactions are discontinuous. One model is a parasite-hyperparasite system designed to capture the essence of biological control and the other is a host-parasite-hyperparasite system that incorporates many more features of the population dynamics. Two types of-discontinuity are included in the models. One corresponds to a pulse of new parasites at harvest and the other reflects the discontinuous presence of the host due to planting and harvesting. Such discontinuities are characteristic of many ecosystems involving parasitism or other interactions with an annual host. The;he models are tested against data fi om an experiment investigating the persistent biological control of the fungal plant parasite of lettuce Sclerotinia minor by the fungal hyperparasite Sporidesmium sclerotivorum, over successive crops. Using a combination of mathematical analysis, model fitting and parameter estimation, the factors that contribute the observed persistence of the parasite are examined. Analytical results show that repeated planting and harvesting of the host allows the parasite to persist by maintaining a quantity of host tissue in the system on which the parasite can reproduce. When the host dynamics are not included explicitly in the model, ne demonstrate that homogeneous mixing fails to predict the persistence of the parasite population, while incorporating spatial heterogeneity by allowing for heterogeneous mixing prevents fade-out. Including the host dynamics lessens the effect of heterogeneous mixing on persistence, though the predicted values for the parasite population are closer to the observed values. An alternative hypothesis for persistence involving a stepped change in rates of infection is also tested and model fitting is used to show that: changes in some environmental conditions may contribute to parasite persistence. The importance of disturbances and periodic forcing in models for interacting populations is discussed. [References: 54]
机译:大多数生态学和流行病学模型都描述了种群之间具有连续不间断交互作用的系统。但是,许多系统都受到生态干扰,例如与季节性作物的种植和收获有关的干扰。在本文中,我们介绍了宿主-寄生虫-超寄生虫系统,作为在宿主-寄生虫相互作用不连续的扰动环境中进行生物控制的模型。一种模型是旨在捕获生物防治本质的寄生虫-超寄生虫系统,另一种模型是包含种群动态更多特征的宿主-寄生虫-超寄生虫系统。模型中包括两种不连续性。一个对应于收获时一波新寄生虫的脉冲,另一个对应于由于种植和收获而寄主的不连续存在。这种不连续性是许多生态系统的特征,涉及寄生或与一年生寄主的其他相互作用。在研究连续性作物上真菌超高寄生菌Sporidesmium sclerotivorum对生菜小核盘菌真菌植物寄生虫的持久生物学控制的实验中,对模型进行了测试。使用数学分析,模型拟合和参数估计的组合,检查了导致观察到的寄生虫持久性的因素。分析结果表明,重复种植和收获宿主可以通过在系统中维持一定数量的宿主组织(寄生虫可在其上繁殖)而使寄生虫得以持久。当模型中未明确包含宿主动态时,ne证明均匀混合无法预测寄生虫种群的持久性,同时通过允许异质混合而纳入空间异质性可防止淡出。尽管寄生虫种群的预测值更接近于观测值,但包含宿主动力学可以减轻异质混合对持久性的影响。还测试了持久性的另一种假设,即涉及感染率的逐步变化,并且模型拟合用于显示:在某些环境条件下的变化可能会导致寄生虫持久性。讨论了在交互种群模型中扰动和周期性强迫的重要性。 [参考:54]

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