强效含氮乳草毒素受土壤氮和食草动物诱导的防御的不同调节。

IF 2.2 3区 环境科学与生态学 Q4 BIOCHEMISTRY & MOLECULAR BIOLOGY
Journal of Chemical Ecology Pub Date : 2024-11-01 Epub Date: 2024-10-29 DOI:10.1007/s10886-024-01546-2
Anurag A Agrawal, Amy P Hastings, Christophe Duplais
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引用次数: 0

摘要

关于土壤氮(N)对植物化学防御能力的影响,人们已经提出了很多理论并进行了测试。在乳草(Asclepias spp.)产生的数百种不同的卡尔德内酯毒素中,含氮的很少,但这些毒素似乎对专门的食草动物最具毒性。由于乳草叶片中同时存在含 N 和不含 N 的卡尔德内酯毒素,而且很可能有不同的生物合成过程,因此它们为解决毒素表达驱动因素的假设提供了机会。我们测试了土壤氮和食草动物破坏对两种生命史策略不同的乳草(Asclepias syriaca 和 A. curassavica)的豆固醇含量的影响,以及它们叶片的毒性。特别是针对帝王斑蝶(Danaus plexippus)和抗性较弱的王蝶(D. gilippus)的目标酶(从神经组织中提取的 Na+/K+-ATP 酶)测试了叶片提取物。增加土壤中的氮可提高 Asclepias syriaca 的生物量,但对豆内酯的影响较弱,包括导致 N-豆内酯(labriformin)的显著减少;帝王斑毛虫的取食可强烈诱导 N-豆内酯(labriformin)、其前体和豆内酯总量的增加。相反,土壤中的氮对 A. curassavica 的生物量影响不大,但却是增加 N-硬脂酚类化合物(香芹酚、草芹酚及其前体)的主要驱动力;毛虫的诱导作用很弱。蝴蝶酶测定显示,破坏诱导的豆蔻内酯大大增加了这两种乳草对两种蝴蝶的毒性,从而抵消了土壤氮对豆蔻内酯浓度和组成的影响。虽然这两种奶草在生长和特定贲门醇内酯的分配上对土壤氮的反应不同,但叶片对蝴蝶 Na+/K+-ATP 酶的毒性主要是由食草动物诱导的防御所驱动的。因此,生物和非生物因素都会影响植物化学防御表达的组成,而它们的相对重要性可能取决于植物的生活史差异。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Potent Nitrogen-containing Milkweed Toxins are Differentially Regulated by Soil Nitrogen and Herbivore-induced Defense.

Theories have been widely proposed and tested for impacts of soil nitrogen (N) on phytochemical defenses. Among the hundreds of distinct cardenolide toxins produced by milkweeds (Asclepias spp.), few contain N, yet these appear to be the most toxic against specialist herbivores. Because N- and non-N-cardenolides coexist in milkweed leaves and likely have distinct biosynthesis, they present an opportunity to address hypotheses about drivers of toxin expression. We tested effects of soil N and herbivore-damage on cardenolide profiles of two milkweed species differing in life-history strategies (Asclepias syriaca and A. curassavica), and the toxicity of their leaves. In particular leaf extracts were tested against the target enzymes (Na+/K+-ATPase extracted from neural tissue) from both monarch butterflies (Danaus plexippus) as well as less cardenolide-resistant queen butterflies, D. gilippus. Increasing soil N enhanced biomass of Asclepias syriaca but had weak effects on cardenolides, including causing a significant reduction in the N-cardenolide labriformin; feeding by monarch caterpillars strongly induced N-cardenolides (labriformin), its precursors, and total cardenolides. Conversely, soil N had little impact on A. curassavica biomass, but was the primary driver of increasing N-cardenolides (voruscharin, uscharin and their precursors); caterpillar induction was weak. Butterfly enzyme assays revealed damage-induced cardenolides substantially increased toxicity of both milkweeds to both butterflies, swamping out effects of soil N on cardenolide concentration and composition. Although these two milkweed species differentially responded to soil N with allocation to growth and specific cardenolides, leaf toxicity to butterfly Na+/K+-ATPases was primarily driven by herbivore-induced defense. Thus, both biotic and abiotic factors shape the composition of phytochemical defense expression, and their relative importance may be dictated by plant life-history differences.

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来源期刊
Journal of Chemical Ecology
Journal of Chemical Ecology 环境科学-生化与分子生物学
CiteScore
5.10
自引率
4.30%
发文量
58
审稿时长
4 months
期刊介绍: Journal of Chemical Ecology is devoted to promoting an ecological understanding of the origin, function, and significance of natural chemicals that mediate interactions within and between organisms. Such relationships, often adaptively important, comprise the oldest of communication systems in terrestrial and aquatic environments. With recent advances in methodology for elucidating structures of the chemical compounds involved, a strong interdisciplinary association has developed between chemists and biologists which should accelerate understanding of these interactions in nature. Scientific contributions, including review articles, are welcome from either members or nonmembers of the International Society of Chemical Ecology. Manuscripts must be in English and may include original research in biological and/or chemical aspects of chemical ecology. They may include substantive observations of interactions in nature, the elucidation of the chemical compounds involved, the mechanisms of their production and reception, and the translation of such basic information into survey and control protocols. Sufficient biological and chemical detail should be given to substantiate conclusions and to permit results to be evaluated and reproduced.
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