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纳米级铜对水生植物的影响——在具有环境相关性的条件下,对缺乏和亚致死毒性的生物化学和生物物理机制进行比较。

Effects of nanomolar copper on water plants--comparison of biochemical and biophysical mechanisms of deficiency and sublethal toxicity under environmentally relevant conditions.

机构信息

Universität Konstanz, Mathematisch-Naturwissenschaftliche Sektion, Fachbereich Biologie, D-78457 Konstanz, Germany.

出版信息

Aquat Toxicol. 2013 Sep 15;140-141:27-36. doi: 10.1016/j.aquatox.2013.05.008. Epub 2013 May 18.

DOI:10.1016/j.aquatox.2013.05.008
PMID:23747550
Abstract

Toxicity and deficiency of essential trace elements like Cu are major global problems. Here, environmentally relevant sub-micromolar concentrations of Cu (supplied as CuSO4) and simulations of natural light- and temperature cycles were applied to the aquatic macrophyte Ceratophyllum demersum. Growth was optimal at 10nM Cu, while PSII activity (Fv/Fm) was maximal around 2 nM Cu. Damage to the PSII reaction centre was the first target of Cu toxicity, followed by disturbed regulation of heat dissipation (NPQ). Only after that, electron transport through PSII (ΦPSII) was inhibited, and finally chlorophylls decreased. Copper accumulation in the plants was stable until 10nM Cu in solution, but strongly increased at higher concentrations. The vein was the main storage site for Cu up to physiological concentrations (10nM). At toxic levels it was also sequestered to the epidermis and mesophyll until export from the vein became inhibited, accompanied by inhibition of Zn uptake. Copper deficiency led to a complete stop of growth at "0"nM Cu after 6 weeks. This was accompanied by high starch accumulation although electron flow through PSII (ΦPSII) decreased from 2 weeks, followed by decrease in pigments and increase of non photochemical quenching (NPQ). Release of Cu from the plants below 10nM Cu supply in the nutrient solution indicated lack of high-affinity Cu transporters, and on the tissue level copper deficiency led to a re-distribution of zinc.

摘要

毒性和必需微量元素(如铜)的缺乏是全球性的主要问题。在这里,应用环境相关的亚微米级浓度的铜(以 CuSO4 的形式提供)和自然光照及温度循环的模拟来处理水生大型植物金鱼藻。在 10nM 的铜浓度下,生长最佳,而 PSII 活性(Fv/Fm)在大约 2nM 的铜浓度下达到最大值。PSII 反应中心的损伤是铜毒性的第一个靶标,随后是热耗散(NPQ)的调节紊乱。只有在这之后,PSII 中的电子传递(ΦPSII)才会受到抑制,最后叶绿素才会减少。植物中铜的积累在溶液中达到 10nM 时保持稳定,但在更高浓度时会强烈增加。叶脉是铜的主要储存部位,直到生理浓度(10nM)。在毒性水平下,它也会被隔离到表皮和叶肉中,直到叶脉中的铜输出被抑制,同时锌的吸收也受到抑制。铜缺乏会导致在“0”nM 铜浓度下 6 周后完全停止生长。这伴随着高淀粉的积累,尽管 PSII(ΦPSII)的电子流从第 2 周开始减少,随后色素减少,非光化学猝灭(NPQ)增加。在营养液中低于 10nM Cu 供应时,从植物中释放 Cu 表明缺乏高亲和力的 Cu 转运蛋白,而在组织水平上,铜缺乏会导致锌的重新分布。

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