Department of Chemistry, University of Quebec in Montreal, C.P. 8888, Succ. Centre-Ville, Montreal, Quebec, Canada H3C 3P8.
J Photochem Photobiol B. 2012 May 2;110:9-14. doi: 10.1016/j.jphotobiol.2012.02.003. Epub 2012 Feb 15.
In natural aquatic ecosystems, temperature conditions may undergo changes depending on the depth of the water column or micro-environmental conditions. In this study, copper effect on the photosynthetic performance of Chlorella vulgaris was investigated at different temperatures by using chlorophyll a fluorescence transients and fluorescence imaging parameters. Copper as a pollutant is known to be an inhibitor of photosystem II (PSII) photochemistry; therefore it was important to know how the change of temperature may alter this effect. PSII photochemistry was investigated when C. vulgaris, affected by different copper concentrations, was exposed to 24, 28 and 31 °C. Increase of temperature induced higher alterating effects to PSII quantum yield, primary photosynthetic electron transport from water splitting system and consequently higher decrease of total photosynthetic performance if compared to copper effect alone. Additional temperature effect to copper inhibition increased energy dissipation via non-photochemical pathway. In this study we indicated that, when C. vulgaris changes temperature conditions, inhibitory effect of copper also undergoes changes. For natural aquatic system we may suppose, when algae are distributed at different depths of water column, that toxicity effect will be dependent to the temperature conditions of the site.
在自然水生生态系统中,水温条件可能会随水层深度或微环境条件而变化。在这项研究中,通过叶绿素 a 荧光瞬变和荧光成像参数,研究了铜在不同温度下对普通小球藻光合作用性能的影响。众所周知,铜作为污染物是光合作用系统 II(PSII)光化学的抑制剂;因此,了解温度变化如何改变这种影响非常重要。当普通小球藻受到不同铜浓度的影响并暴露于 24、28 和 31°C 时,研究了 PSII 光化学。与单独的铜效应相比,温度升高会导致 PSII 量子产率、从水分解系统的初级光合作用电子传递更高的交替效应,从而导致总光合作用性能更高的下降。对铜抑制作用的额外温度效应会通过非光化学途径增加能量耗散。在这项研究中,我们指出,当普通小球藻改变温度条件时,铜的抑制作用也会发生变化。对于自然水生系统,我们可以假设,当藻类分布在水层的不同深度时,毒性效应将取决于该地点的温度条件。