Siemann Evan, DeWalt Saara J, Zou Jianwen, Rogers William E
Biosciences Department, Rice University, Houston, TX 77005 USA.
Department of Biological Sciences, Clemson University, Clemson SC 29634 USA.
AoB Plants. 2016 Dec 30;9(1). doi: 10.1093/aobpla/plw087.
The success of invasive plants may reflect environmental differences in their native and introduced ranges including both abiotic and biotic conditions, such as release from aboveground herbivory. However, in response to these novel conditions, plants from invasive populations may have higher growth rates and lower defense levels compared to those in the native range. This may contribute to their success in the introduced range but perhaps not in the native range. Here, we grew 1000 Triadica sebifera plants from 14 native and introduced populations in seven common gardens with unmanaged background vegetation for three growing seasons in three geographic venues that varied in T. sebifera status and insect herbivore communities: Texas -T. sebifera is invasive, low levels of generalist herbivory; Hawaii - T. sebifera introduced but not invasive, high levels of generalist herbivory from exotic herbivores; China - native range, both generalist and specialist herbivores. We suppressed aboveground insects with insecticide on half the plants. Aboveground damage in the first growing season was lowest in Texas and insecticide sprays reduced damage in China. At the end of the first growing season, plants were tallest on average in China and shortest in Hawaii. However, height in later years and mass were highest on average in Texas and lowest in Hawaii. However, there was large variation in damage and plant performance among gardens within venues. Our results suggest that more rapid aboveground growth rates contribute to T. sebifera's success in both the invasive and native ranges independent of aboveground herbivory. However, strong variation among sites indicates that T. sebifera plants from invasive populations only have a strong advantage in a subset of sites in Texas.
入侵植物的成功可能反映出其原生地和引入地在环境上的差异,包括非生物和生物条件,例如摆脱了地上食草动物的啃食。然而,面对这些新环境,与原生地的植物相比,入侵种群的植物可能具有更高的生长速率和更低的防御水平。这可能有助于它们在引入地取得成功,但在原生地可能并非如此。在此,我们在七个拥有未管理背景植被的共同花园中,种植了来自14个原生和引入种群的1000株乌桕,在三个地理地点进行了三个生长季节的种植,这些地点在乌桕的状态和昆虫食草动物群落方面各不相同:德克萨斯州——乌桕具有入侵性,泛食性食草动物水平较低;夏威夷——乌桕已引入但不具入侵性,外来食草动物的泛食性食草动物水平较高;中国——原生地,既有泛食性食草动物又有专食性食草动物。我们用杀虫剂处理了一半植株以抑制地上昆虫。在第一个生长季节,地上部分的损害在德克萨斯州最低,在中国,杀虫剂喷雾减少了损害。在第一个生长季节结束时,植株平均在中国最高,在夏威夷最矮。然而,在随后几年中,植株高度和质量平均在德克萨斯州最高,在夏威夷最低。然而,在各地点内的花园中,损害和植株表现存在很大差异。我们的结果表明,更快的地上生长速率有助于乌桕在入侵地和原生地都取得成功,且与地上食草动物无关。然而,各地点之间的强烈差异表明,来自入侵种群的乌桕植株仅在德克萨斯州的一部分地点具有强大优势。