College of Natural Resources and Environment, Northwest A & F University, Yangling, 712100, China.
Australian Rivers Institute, School of Environment and Science, Griffith University, Nathan, Queensland, 4111, Australia.
Biol Rev Camb Philos Soc. 2018 Aug;93(3):1399-1420. doi: 10.1111/brv.12401. Epub 2018 Feb 22.
Morphological evolution from a unicellular to multicellular state provides greater opportunities for organisms to attain larger and more complex living forms. As the most common freshwater cyanobacterial genus, Microcystis is a unicellular microorganism, with high phenotypic plasticity, which forms colonies and blooms in lakes and reservoirs worldwide. We conducted a systematic review of field studies from the 1990s to 2017 where Microcystis was dominant. Microcystis was detected as the dominant genus in waterbodies from temperate to subtropical and tropical zones. Unicellular Microcystis spp. can be induced to form colonies by adjusting biotic and abiotic factors in laboratory. Colony formation by cell division has been induced by zooplankton filtrate, high Pb concentration, the presence of another cyanobacterium (Cylindrospermopsis raciborskii), heterotrophic bacteria, and by low temperature and light intensity. Colony formation by cell adhesion can be induced by zooplankton grazing, high Ca concentration, and microcystins. We hypothesise that single cells of all Microcystis morphospecies initially form colonies with a similar morphology to those found in the early spring. These colonies gradually change their morphology to that of M. ichthyoblabe, M. wesenbergii and M. aeruginosa with changing environmental conditions. Colony formation provides Microcystis with many ecological advantages, including adaption to varying light, sustained growth under poor nutrient supply, protection from chemical stressors and protection from grazing. These benefits represent passive tactics responding to environmental stress. Microcystis colonies form at the cost of decreased specific growth rates compared with a unicellular habit. Large colony size allows Microcystis to attain rapid floating velocities (maximum recorded for a single colony, ∼ 10.08 m h ) that enable them to develop and maintain a large biomass near the surface of eutrophic lakes, where they may shade and inhibit the growth of less-buoyant species in deeper layers. Over time, accompanying species may fail to maintain viable populations, allowing Microcystis to dominate. Microcystis blooms can be controlled by artificial mixing. Microcystis colonies and non-buoyant phytoplankton will be exposed to identical light conditions if they are evenly distributed over the water column. In that case, green algae and diatoms, which generally have a higher growth rate than Microcystis, will be more successful. Under such mixing conditions, other phytoplankton taxa could recover and the dominance of Microcystis would be reduced. This review advances our understanding of the factors and mechanisms affecting Microcystis colony formation and size in the field and laboratory through synthesis of current knowledge. The main transition pathways of morphological changes in Microcystis provide an example of the phenotypic plasticity of organisms during morphological evolution from a unicellular to multicellular state. We emphasise that the mechanisms and factors influencing competition among various close morphospecies are sometimes paradoxical because these morphospecies are potentially a single species. Further work is required to clarify the colony-forming process in different Microcystis morphospecies and the seasonal variation in this process. This will allow researchers to grow laboratory cultures that more closely reflect field morphologies and to optimise artificial mixing to manage blooms more effectively.
从单细胞到多细胞状态的形态进化为生物提供了更大的机会,使其能够获得更大、更复杂的生活形式。微囊藻作为最常见的淡水蓝藻属,是一种单细胞微生物,具有高度的表型可塑性,它在世界各地的湖泊和水库中形成群体并大量繁殖。我们对 20 世纪 90 年代至 2017 年期间的野外研究进行了系统回顾,其中微囊藻占主导地位。在从温带到亚热带和热带地区的水体中都检测到了以微囊藻为主导的属。在实验室中,通过调整生物和非生物因素,可以诱导单细胞微囊藻形成群体。通过浮游动物滤食、高 Pb 浓度、另一种蓝藻(铜绿微囊藻)、异养细菌以及低温和低光强,可以诱导细胞分裂形成群体。通过浮游动物摄食、高 Ca 浓度和微囊藻毒素可以诱导细胞黏附形成群体。我们假设所有微囊藻形态种的单细胞最初都会形成与早春相似的形态的群体。随着环境条件的变化,这些群体逐渐演变成 M. ichthyoblabe、M. wesenbergii 和 M. aeruginosa 的形态。群体形成使微囊藻具有许多生态优势,包括适应不同的光照、在营养供应不足的情况下持续生长、免受化学胁迫和免受摄食的影响。这些益处代表了对环境胁迫的被动策略。与单细胞习性相比,群体形成会降低微囊藻的特定生长速率。大的群体大小使微囊藻能够获得快速的漂浮速度(单个群体的最大记录速度约为 10.08 m h),这使它们能够在富营养化湖泊的表面附近形成和维持大量生物量,在那里它们可以遮荫并抑制深层中浮力较小的物种的生长。随着时间的推移,伴随的物种可能无法维持存活种群,从而使微囊藻占主导地位。可以通过人工混合来控制微囊藻水华。如果微囊藻群体和非浮性浮游藻类在水柱中均匀分布,它们将暴露在相同的光照条件下。在这种情况下,通常比微囊藻生长速度更快的绿藻和硅藻将更成功。在这种混合条件下,其他浮游藻类分类群可能会恢复,微囊藻的优势地位将会降低。通过综合当前的知识,本综述增进了我们对影响野外和实验室中微囊藻群体形成和大小的因素和机制的理解。微囊藻形态变化的主要转变途径为生物从单细胞到多细胞状态的形态进化过程中的表型可塑性提供了一个例子。我们强调,影响不同近缘形态种之间竞争的机制和因素有时是矛盾的,因为这些形态种可能是单一的物种。需要进一步的工作来阐明不同微囊藻形态种的群体形成过程以及该过程的季节性变化。这将使研究人员能够培养更能反映野外形态的实验室培养物,并优化人工混合以更有效地管理水华。