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Relationships between primary production of phytoplankton and environmental factors in a shallow brackish lake

机译:浅咸湖中浮游植物初级生产力与环境因子的关系

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Brackish lakes and estuaries are strongly affected by both terrestrial and oceanic factors because of the complex mixing of fresh water and seawater, and their characteristic fluctuations in water quality differ from those of freshwater lakes or the oceans (McLusky 1989). In brackish water areas, there are large fluctuations in salinity with the tides and freshwater discharge, which play a key role in establishing the distribution and dynamics of the physico-chemical water quality. Fluctuations of salinity influence the distribution of biological species. When a strong halocline forms in brackish waters, the vertical mixing of substances between the water layers above and below is limited (Lougee et al. 2002, Ueda et al. 2005). Therefore, water quality and characterization of an ecosystem in a brackish lake differ in its upper and lower layers.rnBrackish Lake Obuchi in Rokkasho, Japan, is bordered by a nuclear spent-fuel reprocessing plant. Small amounts of radionuclides (such as ~(85)Kr, ~3H, ~(14)C, and ~(129)I) are released from the reprocessing plant and may enter this lake from the ocean by means of tides, from the land via rivers, and from the atmosphere by fallout. The behavior of these radionuclides is strongly influenced by environmental factors in the lake ecosystem. Therefore, the impact of radioactive substances released from the reprocessing plant must be evaluated to assess the safety of the surrounding environment and to develop a radionuclide transfer model for this lake. We developed the transfer model for radionuclides to evaluate the physical-biological interactions in terms of an estuarine lower-trophic (phytoplankton and zooplankton) ecosystem (Ueda et al. 2006); however, the calculated precision of a primary production of phytoplankton is slightly low. To improve the reproducibility of our model, the parameter related to a primary production of phytoplankton in the field must be obtained.rnIn this study we clarified the vertical distributions of primary production of phytoplankton and environmental factors (such as water quality, water temperature, salinity, and irradi-ance) in Lake Obuchi to obtain the parameter related to a primary production in the field. Moreover, we investigated the relationship between photosynthesis and the irradiance (P-I curve) curve in the upper and lower layers by the ~(13)C technique.
机译:由于淡水和海水的复杂混合,咸淡的湖泊和河口受陆地和海洋因素的强烈影响,其水质的特征性波动不同于淡水湖泊或海洋(McLusky 1989)。在微咸水地区,潮汐和淡水的盐度波动很大,这对确定理化水质的分布和动态起着关键作用。盐度的波动会影响生物物种的分布。当在咸淡水中形成浓卤盐时,上下两层水之间的垂直混合受到限制(Lougee等,2002; Ueda等,2005)。因此,咸淡湖的水质和生态系统的特征在其上层和下层都不同。日本六所庄的咸淡湖小渊池以核废燃料后处理厂为边界。从后处理厂释放出少量放射性核素(例如〜(85)Kr,〜3H,〜(14)C和〜(129)I),并可能通过潮汐从海洋中进入该湖。通过河流降落,通过大气层降落。这些放射性核素的行为受到湖泊生态系统中环境因素的强烈影响。因此,必须评估从后处理厂释放的放射性物质的影响,以评估周围环境的安全性,并为该湖开发放射性核素转移模型。我们开发了放射性核素的转移模型,以评估河口低营养(浮游植物和浮游动物)生态系统的物理-生物相互作用(Ueda等,2006)。但是,浮游植物初级生产的计算精度略低。为了提高模型的可重复性,必须获得与浮游植物初生相关的参数。在本研究中,我们阐明了浮游植物初生的垂直分布和环境因素(例如水质,水温,盐度) (和辐照度),以获取与该领域的初级生产相关的参数。此外,我们通过〜(13)C技术研究了上层和下层光合作用与辐照度(P-I曲线)之间的关系。

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