入侵物种:

William D. Holland
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引用次数: 0

摘要

外来物种随处可见。它们散布在世界各地,通过空气、水和陆地传播,甚至可能落在你的后院。由于入侵物种经常与本地物种的消失联系在一起,它们被公众和科学家们称为“外来物种”,这是一个可怕的名声。其中一些受到了媒体的广泛关注,比如关岛的棕色树蛇,堵塞五大湖的斑马贻贝,遍布澳大利亚的兔子,以及葛藤或“吃南方的藤蔓”。他们的成功让许多人感到困惑,但过去十年的最新研究指出了一个可能对入侵物种传播至关重要的新因素:表型可塑性。表型可塑性是指生物体通过物理性状或表型的变化来适应环境变化的能力。这种现象间接来自基因型,基因型是决定特定表型的基因。为了使自然选择作用于这些物种,入侵物种的种群必须作用于遗传基质。通常,由于需要足够的加性遗传变异(AGV),在物种爆发之前观察到初始滞后。这使得环境对表型表达的遗传底物积累(1)。与静态表型相比,表型的变化可能使生物体具有更高的适应水平(2)。此外,更高水平的表型可塑性使生物能够在新环境中定植。由于种群规模小,入侵物种经常进入遗传多样性较低的新环境,但高表型可塑性可能有助于物种通过快速进化应对新的胁迫(2)。可塑性有助于生物在广泛的环境中表达有利的表型,支持在某些物种中观察到的生态宽度与表型可塑性之间的正相关(3,4)。再加上杂交,可塑性促进了进一步的遗传变异和新的基因相互作用(1)。当入侵物种到达新的栖息地时,具有传播能力或高生理耐受性的生物受到进化的青睐,从而推动了对天敌可能抑制的有益性状的选择(1,5)。事实上,已经注意到,与本地栖息地相比,在外来栖息地,入侵植物倾向于通过产生更多种子来更有力地增殖——这是反应规范变化的一个例子,或者是特定基因型表型表达的一个例子(5)。自17世纪被引入美国以来,丝绒叶(Abutilon theophrasti)已经进化出了许多不同的策略来应对不同竞争来源的存在(1)。具体来说,丝绒叶种群往往是塑料的,以响应光质量,以便超过大豆。但在较高的玉米植株存在的情况下,可塑性对这些植物不利(5)。表型可塑性可以被认为是一个问题,因为它允许入侵物种进化出抵抗人类试图根除的能力,如杀虫剂和除草剂。有关入侵物种的政策往往忽视了由于根除工作设计不当而造成的抗药性的后果。因此,进一步的研究应旨在阐明导致对入侵害虫控制方法产生抗性的表型变化。这样的调查可以让我们解决根除入侵物种的挑战,同时最大限度地减少造成弊大于利的可能性。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Invasive Species:
I nvasive species can be found everywhere. Scattered across the world, they have traveled by air, water, and land and may have even landed in your backyard. Because invasive species are often associated with the disappearance of native species, they have garnered a dreadful reputation as being “foreign” by the public and scientists alike. Some have received a lot of attention from the media, such as the brown tree snakes in Guam, zebra mussels clogging the Great Lakes, rabbits overrunning Australia, and the kudzu or “the vine that ate the South.” Their success has baffled many, but recent studies in the past decade have pointed to a new factor that may potentially be crucial to the spread of invasive species: phenotypic plasticity. Phenotypic plasticity refers to the ability for organisms to adapt to environmental changes through changes in physical traits or phenotype. This phenomenon draws indirectly from genotype, which are the genes that dictate a particular phenotype. In order for natural selection to act on these species, populations of invasive species must act upon a genetic substrate. Often times, an initial lag is observed before the explosion of a species because of the need of sufficient additive genetic variance (AGV). This allows the accumulation of genetic substrate for phenotypic expression on which the environment acts (1). Changes in phenotype may give organisms a higher fitness level compared to those with static phenotypes (2). Moreover, higher levels of phenotypic plasticity enable colonization in new environments. Invasive species often come into new environments with low genetic diversity because of small population sizes, but high phenotypic plasticity may aid the species to cope with new stresses through rapid evolution (2). Plasticity helps organisms express advantageous phenotypes in a wide range of environments, supporting the positive correlation between ecological breadth and phenotypic plasticity observed in some species (3,4). Coupled with hybridization, plasticity facilitates further genetic variance and novel gene interactions (1). When invasive species arrive in new habitats, organisms with dispersal capacity or high physiological tolerance are favored by evolution, driving the selection for beneficial traits that natural enemies may have suppressed (1,5). In fact, it has been noted that in foreign habitats compared to native habitats, invasive plants tend to proliferate more vigorously by producing more seeds—an example of the changing reaction norm, or expression of phenotypes by a particular genotype (5). As an example of the evolution of phenotypic plasticity, the velvetleaf (Abutilon theophrasti) has evolved a number of distinct strategies to proliferate in the presence of different sources of competition ever since it was introduced to the United States in the 17th century (1). Specifically, velvetleaf populations tend to be plastic in response to light quality in order to outgrow soybeans, but plasticity is not advantageous to these plants in the presence of the taller corn plants (5). Phenotypic plasticity can be considered a problem because it allows invasive species to evolve resistance against human attempts at eradication, such as pesticides and herbicides. Policies regarding invasive species often overlook the consequences of resistance caused by poorly designed efforts at eradication. As a result, further studies should be directed toward elucidating the phenotypic changes that lead to the development of resistance in response to methods used to control invasive pests. Such investigations can allow us to tackle the challenge of eradicating invasive species while minimizing the potential to cause more harm than good.
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