{"title":"In Situ Production of Charophyte Communities under Reduced Light Conditions in a Brackish-Water Ecosystem","authors":"Anastasiia Kovtun-Kante, K. Torn, J. Kotta","doi":"10.3176/ECO.2014.1.03","DOIUrl":null,"url":null,"abstract":"INTRODUCTION Charophyte communities are an important element in shallow enclosed fresh- and brackish-water ecosystems (Mathieson and Nienhuis, 1991; van den Berg et al., 1998; Pelechaty et al., 2006). They provide shelter and habitat for numerous species including epiphytic microalgae, filamentous macroalgae, as well as various crustacean and insect species (Linden et al., 2003; Schmieder et al., 2006; Torn et al., 2010). Besides, charophytes are an important component in the food web as part of the diet of benthic invertebrates (Kotta et al., 2004, 2013), waterfowl (Noordhuis et al., 2002; Schmieder et al., 2006), and fish and fish larvae (de Winton et al., 2002; Dugdale et al., 2006). Declining distribution and diversity of charophytes have been observed in many regions worldwide including the brackish Baltic Sea (Blindow, 2000, 2001; Schubert and Blindow 2003; Munsterhjelm, 2005). Eutrophication is assumed to be the most important threat to charophytes causing their decline (e.g. Blindow, 1992; Auderset Joye et al., 2002). The main effect associated with eutrophication is the bloom of ephemeral planktonic algae, which leads to increased sedimentation, water turbidity and, as a result, reduced light availability. The shortage of light may reduce the photosynthetic production and growth of charophytes down to the level where their sustainable development becomes impossible (Blindow et al., 2002; Johnsen and Sosik, 2004; Hautier et al., 2009; Dickey et al., 2011). On the other hand, charophytes often prefer soft bottom habitats where even moderate wind may cause sediment resuspension and sedimentation of particles on the plant surface. In such habitats underwater light climate is naturally very variable (Schneider et al., 2006 and references therein). Thus, charophytes are adapted to periodic stress of low light intensities. Nevertheless, the interactive effect of elevated eutrophication and weather variables may result in poorer light conditions than expected from their separate effects (Blindow et al., 2003; Kling et al., 2003). So far, the studies concerning photosynthesis of charophytes are mainly based on laboratory experiments with either detached pieces or single individuals (e.g. Blindow et al., 2003; Marquardt and Schubert, 2009). Very few have been carried out in the natural environments, especially in brackish bodies of water. As compared to their freshwater counterparts, charophytes are often naturally stressed at elevated salinity and therefore are expected to respond differently to changes in light conditions (e.g. Blindow et al., 2003). The existing data on in situ primary production of charophytes related to light limitation are scarce and hardly comparable because of difference in methodologies and the environmental conditions among habitats (Kufel and Kufel, 2002). Light is a key limiting factor for photosynthetic production in aquatic environments (Kurtz et al., 2003; Asaeda et al., 2004, Binzer et al., 2006; Zhang et al., 2010). Earlier experimental studies carried out at the community level have also shown that canopy density and canopy structure significantly affect the photosynthetic production of marine macroalgae (Middelboe et al., 2006). This suggests that macroalgal communities are largely light-limited and such light limitation increases with canopy height and/or community biomass (Parnoja et al., 2013). Altough the photosynthetic production of marine macroalgae at the community level has been increasingly studied (Middelboe and Binzer, 2004; Middelboe et al., 2006; Parnoja et al., 2013), to the best of our knowledge, there is only a single study on charophyte communities (Libbert and Walter, 1985). Based on the above, our goal was to determine the primary production of a charophyte community under manipulated in situ light conditions. We hypothesized that (a) the community would have higher responses under more severe light limitation and (b) the recovery of charophyte photosynthetic performance would be faster under less severe disturbances. …","PeriodicalId":262667,"journal":{"name":"Estonian Journal of Ecology","volume":"17 1","pages":"0"},"PeriodicalIF":0.0000,"publicationDate":"2014-03-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"14","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Estonian Journal of Ecology","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.3176/ECO.2014.1.03","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 14
Abstract
INTRODUCTION Charophyte communities are an important element in shallow enclosed fresh- and brackish-water ecosystems (Mathieson and Nienhuis, 1991; van den Berg et al., 1998; Pelechaty et al., 2006). They provide shelter and habitat for numerous species including epiphytic microalgae, filamentous macroalgae, as well as various crustacean and insect species (Linden et al., 2003; Schmieder et al., 2006; Torn et al., 2010). Besides, charophytes are an important component in the food web as part of the diet of benthic invertebrates (Kotta et al., 2004, 2013), waterfowl (Noordhuis et al., 2002; Schmieder et al., 2006), and fish and fish larvae (de Winton et al., 2002; Dugdale et al., 2006). Declining distribution and diversity of charophytes have been observed in many regions worldwide including the brackish Baltic Sea (Blindow, 2000, 2001; Schubert and Blindow 2003; Munsterhjelm, 2005). Eutrophication is assumed to be the most important threat to charophytes causing their decline (e.g. Blindow, 1992; Auderset Joye et al., 2002). The main effect associated with eutrophication is the bloom of ephemeral planktonic algae, which leads to increased sedimentation, water turbidity and, as a result, reduced light availability. The shortage of light may reduce the photosynthetic production and growth of charophytes down to the level where their sustainable development becomes impossible (Blindow et al., 2002; Johnsen and Sosik, 2004; Hautier et al., 2009; Dickey et al., 2011). On the other hand, charophytes often prefer soft bottom habitats where even moderate wind may cause sediment resuspension and sedimentation of particles on the plant surface. In such habitats underwater light climate is naturally very variable (Schneider et al., 2006 and references therein). Thus, charophytes are adapted to periodic stress of low light intensities. Nevertheless, the interactive effect of elevated eutrophication and weather variables may result in poorer light conditions than expected from their separate effects (Blindow et al., 2003; Kling et al., 2003). So far, the studies concerning photosynthesis of charophytes are mainly based on laboratory experiments with either detached pieces or single individuals (e.g. Blindow et al., 2003; Marquardt and Schubert, 2009). Very few have been carried out in the natural environments, especially in brackish bodies of water. As compared to their freshwater counterparts, charophytes are often naturally stressed at elevated salinity and therefore are expected to respond differently to changes in light conditions (e.g. Blindow et al., 2003). The existing data on in situ primary production of charophytes related to light limitation are scarce and hardly comparable because of difference in methodologies and the environmental conditions among habitats (Kufel and Kufel, 2002). Light is a key limiting factor for photosynthetic production in aquatic environments (Kurtz et al., 2003; Asaeda et al., 2004, Binzer et al., 2006; Zhang et al., 2010). Earlier experimental studies carried out at the community level have also shown that canopy density and canopy structure significantly affect the photosynthetic production of marine macroalgae (Middelboe et al., 2006). This suggests that macroalgal communities are largely light-limited and such light limitation increases with canopy height and/or community biomass (Parnoja et al., 2013). Altough the photosynthetic production of marine macroalgae at the community level has been increasingly studied (Middelboe and Binzer, 2004; Middelboe et al., 2006; Parnoja et al., 2013), to the best of our knowledge, there is only a single study on charophyte communities (Libbert and Walter, 1985). Based on the above, our goal was to determine the primary production of a charophyte community under manipulated in situ light conditions. We hypothesized that (a) the community would have higher responses under more severe light limitation and (b) the recovery of charophyte photosynthetic performance would be faster under less severe disturbances. …
绿藻群落是浅层封闭淡水和咸淡水生态系统的重要组成部分(Mathieson和Nienhuis, 1991;van den Berg et al., 1998;peelechaty et al., 2006)。它们为许多物种提供了庇护和栖息地,包括附生微藻、丝状大藻以及各种甲壳类和昆虫物种(Linden et al., 2003;Schmieder等人,2006;Torn et al., 2010)。此外,作为底栖无脊椎动物(Kotta et al., 2004,2013)、水禽(Noordhuis et al., 2002;Schmieder等人,2006年),鱼和鱼苗(de Winton等人,2002年;Dugdale et al., 2006)。在世界上许多地区,包括咸淡的波罗的海,已经观察到蕨类植物的分布和多样性下降(Blindow, 2000, 2001;舒伯特和布林道2003;Munsterhjelm, 2005)。富营养化被认为是对蕨类植物最重要的威胁,导致它们的衰退(例如Blindow, 1992;Auderset joy et al., 2002)。与富营养化有关的主要影响是短暂的浮游藻类的大量繁殖,这导致沉积增加,水浑浊,结果是可用光线减少。光照不足可能会使蕨类植物的光合作用产生和生长降低到无法持续发展的水平(Blindow et al., 2002;Johnsen and Sosik, 2004;Hautier et al., 2009;Dickey et al., 2011)。另一方面,绿叶植物往往更喜欢软底栖息地,在那里即使是温和的风也会引起沉积物的再悬浮和颗粒在植物表面的沉积。在这样的栖息地,水下光照气候自然是非常多变的(Schneider et al., 2006和其中的参考文献)。因此,叶绿植物适应低光强度的周期性应力。然而,富营养化程度升高和天气变量的相互作用可能导致光照条件比它们各自的影响所预期的要差(Blindow等人,2003;Kling et al., 2003)。迄今为止,关于蕨类植物光合作用的研究主要是基于分离体或单个个体的实验室实验(如Blindow et al., 2003;马夸特和舒伯特,2009)。很少在自然环境中进行,特别是在微咸水体中。与淡水植物相比,绿叶植物通常在高盐度环境下受到自然胁迫,因此预计会对光照条件的变化做出不同的反应(例如Blindow等人,2003年)。由于不同生境的方法和环境条件的差异,现有的与光照限制有关的蕨类植物原位初级生产的数据很少,而且很难进行比较(Kufel和Kufel, 2002)。光是水生环境中光合作用产生的关键限制因素(Kurtz et al., 2003;Asaeda et al., 2004; Binzer et al., 2006;Zhang等人,2010)。早期在群落水平上进行的实验研究也表明,冠层密度和冠层结构显著影响海洋大型藻类的光合生产(Middelboe et al., 2006)。这表明大型藻群落在很大程度上是受光照限制的,这种光照限制随着冠层高度和/或群落生物量的增加而增加(Parnoja等,2013)。尽管在群落水平上对海洋大型藻类的光合作用生产的研究越来越多(Middelboe和Binzer, 2004;Middelboe et al., 2006;Parnoja et al., 2013),据我们所知,只有一项关于蕨类植物群落的研究(Libbert and Walter, 1985)。在此基础上,我们的目标是确定在受控的原位光照条件下蕨类植物群落的初级产量。我们假设:(a)在更严重的光限制下,群落的响应会更高;(b)在较小的干扰下,叶绿素光合性能的恢复会更快。...