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首页> 外文期刊>Population ecology >Modeling population growth and site specific control of the invasive Lantana camara L. (Verbenaceae) under differing fire regimes
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Modeling population growth and site specific control of the invasive Lantana camara L. (Verbenaceae) under differing fire regimes

机译:模拟不同火势下入侵马Lan丹(马鞭草科)的种群增长和特定地点的控制

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It is at the population level that an invasion either fails or succeeds. Lantana camara L. (Verbenaceae) is a weed of great significance in Queensland Australia and globally but its whole life-history ecology is poorly known. Here we used 3 years of field data across four land use types (farm, hoop pine plantation and two open eucalyptus forests, including one with a triennial fire regime) to parameterise the weed's vital rates and develop size-structured matrix models. Lantana camara in its re-colonization phase, as observed in the recently cleared hoop pine plantation, was projected to increase more rapidly (annual growth rate, X = 3.80) than at the other three sites (1 1.88-2.71). Elasticity analyses indicated that growth contributed more (64.6 %) to 1 than fecundity (18.5 %) or survival (15.5 %), while across size groups, the contribution was of the order: juvenile (19-27 %) > seed (17-28 %) > seedling (16-25 %) > small adult (4-26 %) > medium adult (7-20 %) > large adult (0-20 %). From a control perspective it is difficult to determine a single weak point in the life cycle of lantana that might be exploited to reduce growth below a sustaining rate. The triennial fire regime applied did not alter the population elasticity structure nor resulted in local control of the weed. However, simulations showed that, except for the farm population, periodic burning could work within 4-10 years for control of the weed, but fire frequency should increase to at least once every 2 years. For the farm, site-specific control may be achieved by 15 years if the biennial fire frequency is tempered with increased burning intensity.
机译:入侵是成功还是失败是在人口层面上。马tana丹(马鞭草科)是一种在澳大利亚昆士兰州乃至全球具有重要意义的杂草,但其整个生命史生态学却鲜为人知。在这里,我们使用了3年的田间数据,涵盖了四种土地利用类型(农场,箍松林和两种开放式桉树林,其中一种具有三年生火情),以参数化杂草的生命率并建立了大小结构矩阵模型。如最近清除的箍松林中所观察到的那样,马cam丹卡马拉处于重新定殖阶段,预计将比其他三个地点(1 1.88-2.71)增长得更快(年增长率,X = 3.80)。弹性分析表明,增长对生殖能力的贡献(64.6%)比生殖力(18.5%)或存活率(15.5%)多,而在不同规模的人群中,贡献的顺序是:少年(19-27%)>种子(17- 28%)>幼苗(16-25%)>小成年(4-26%)>中成年(7-20%)>大成年(0-20%)。从控制的角度来看,很难确定马tana丹生命周期中的一个薄弱环节,可以利用该薄弱环节将生长速度降低至低于维持率。三年一次的防火制度并没有改变种群的弹性结构,也没有导致对杂草的局部控制。但是,模拟显示,除农场人口外,定期燃烧可在4-10年内起作用以控制杂草,但火灾频率至少应每两年增加一次。对于农场,如果两年一度的火灾频率随着燃烧强度的增加而调整,则可以在15年内实现特定地点的控制。

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