Heinrich Almut
Scientific Journals, ecomed publishers, 86899, Landsberg, Germany,
Environ Sci Pollut Res Int. 2007 Jan;14 Suppl 1:11-8. doi: 10.1065/espr2007.01.379. Epub 2007 Jan 23.
and Aim. In non-eutrophicated freshwaters, humic substances (HS) pose chemical stresses on aquatic organisms and, hence, separating sensitive from less sensitive or even tolerant species. One of the stresses, identified so far, is the reduction of photosynthetic oxygen production and reduction in growth in freshwater macrophytes and algae. In a previous paper, it has been shown that even closely related coccal green algae responded differently upon identical stress by HS, which is consistent with the hypothesis above. Due to their much simpler cellular ultrastructure, cyanobacteria are supposed to be more sensitive to HS exposure than eukaryote should be. One coccal green algal species (Desmodesmus communis) and one cyanobacterium (Chroococcus minutus) were exposed to four natural organic matter (NOM) isolates. One NOM has been isolated from a brown water lake (Schwarzer See) in Brandenburg State; three were obtained from a comprehensive Scandinavian NOM research project and originated from Norway (Birkenes), Finland (Hietajärvi), and Sweden (Svartberget).
Cultures of D. communis and C. minutus were obtained from the Culture Collection of Algae, Göttingen, and maintained in a common medium. The cultures were non-axenic. The algae and cyanobacteria were exposed under identical conditions to environmentally realistic NOM concentrations. Cell numbers were counted microscopically in Neugebauer cuvettes in triplicates. To avoid limitation by nutrient depletion, the experiments were terminated after 14 to 15 days. Until culture day 12, no growth limitation has been observed in the controls.
All NOM isolates modulated the growth of the algae and cyanobacteria. During the early culture days, there was a slight growth promotion with the coccal green alga and to a much lesser degree with the cyanobacterium. Yet, the major effect were significant reductions in cell yield in both primary producer cultures. C. minutus was much more affected than D. communis. This applies particularly to the three tested Scandinavian NOM isolates, which were effective at concentrations even below 1 mg L-1 DOC.
The growth promoting effect may be due to an increase in bioavailability of some trace nutrients in the presence of NOM, the release of some growth promoting substances by microbial or photochemical processing of the NOM, and/or a hormetic effect. The growth reducing effect can be explained as a herbicide-like mode of action that affects the photosystem II most prevalent by blocking the electron transport chain, absorption of electrons, or production of an internal oxidative stress after processing the bioconcentrated HS. Furthermore, it may be postulated that also photo-toxicity of these HS in the algal cells contributes to the overall toxicity; however, experimental evidence is lacking so far.
Upon exposure to HS, cyanobacteria appear to be much more sensitive than coccal green algae and respond in growth reduction. This high sensitivity of cyanobacteria to HS may explain phytoplankton patterns in the field. Eutrophic, humic-rich lakes do not support the cyanobacterial blooms characteristic of eutrophic, but humic-poor lakes. In the humic-rich systems, raphidophytes or, less frequent, specific coccal greens are more common. Obviously, cyanobacteria appear to be unable to make advantage of their accessory pigments (phycocyanin) to exploit the reddish light prevailing in humic-rich lakes.
. At present, no effective structure can be figured out which may be responsible for the adverse effect on the cyanobacterial species. It is reserved to future research whether or not HS may be applied more specifically (for instance, with elevated moieties of the effective structures) as a natural geochemical to combat cyanobacterial blooms.
背景与目的。在未富营养化的淡水中,腐殖质(HS)会对水生生物造成化学胁迫,从而区分出敏感物种与较不敏感甚至耐受的物种。目前已确定的胁迫之一是淡水大型植物和藻类的光合产氧量降低以及生长减缓。在之前的一篇论文中,已经表明即使是亲缘关系密切的球状绿藻在受到HS相同胁迫时也会有不同反应,这与上述假设一致。由于蓝藻的细胞超微结构简单得多,因此推测它们可能比真核生物对HS暴露更敏感。将一种球状绿藻(普通栅藻)和一种蓝藻(微小色球藻)暴露于四种天然有机物(NOM)分离物中。一种NOM分离自勃兰登堡州的一个褐水湖(施瓦泽湖);另外三种来自一个全面的斯堪的纳维亚NOM研究项目,分别源自挪威(比尔克内斯)、芬兰(希耶塔耶尔维)和瑞典(斯瓦特贝里)。
普通栅藻和微小色球藻的培养物取自哥廷根藻类培养物保藏中心,并在一种通用培养基中培养。培养物并非无菌。藻类和蓝藻在相同条件下暴露于符合环境实际情况的NOM浓度。在诺伊格鲍尔比色管中通过显微镜对细胞数量进行计数,重复三次。为避免因营养耗尽而产生限制,实验在14至15天后终止。直到培养第12天,对照中未观察到生长限制。
所有NOM分离物均调节了藻类和蓝藻的生长。在培养初期,球状绿藻有轻微的生长促进,蓝藻的促进程度则小得多。然而,主要影响是两种初级生产者培养物中的细胞产量显著降低。微小色球藻比普通栅藻受影响大得多。这尤其适用于测试的三种斯堪的纳维亚NOM分离物,它们在浓度甚至低于1 mg L-1 DOC时就有效果。
生长促进作用可能是由于在NOM存在下某些微量营养素的生物可利用性增加、NOM的微生物或光化学处理释放出一些生长促进物质,和/或一种刺激效应。生长抑制作用可以解释为一种类似除草剂的作用模式,通过阻断电子传递链、吸收电子或在处理生物浓缩的HS后产生内部氧化应激,从而对最普遍的光系统II产生影响。此外,可以推测这些HS在藻类细胞中的光毒性也对整体毒性有贡献;然而,目前还缺乏实验证据。
暴露于HS时,蓝藻似乎比球状绿藻敏感得多,并且生长会受到抑制。蓝藻对HS的这种高敏感性可能解释了野外浮游植物的模式。富营养、富含腐殖质的湖泊不会出现富营养但腐殖质含量低的湖泊所特有的蓝藻水华。在富含腐殖质的系统中,针胞藻或较不常见的特定球状绿藻更为常见。显然,蓝藻似乎无法利用其辅助色素(藻蓝蛋白)来利用富含腐殖质湖泊中普遍存在的红光。
目前,尚无法确定哪种有效结构可能对蓝藻物种产生不利影响。HS是否可以更特异性地(例如,具有更高比例的有效结构)作为一种天然地球化学物质来对抗蓝藻水华,有待未来研究。