浅咸淡湖浮游植物初级生产与环境因子的关系

S. Ueda, K. Kondo, Yuki Chikuchi
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引用次数: 1

摘要

由于淡水和海水的复杂混合,咸淡水湖泊和河口受到陆地和海洋因素的强烈影响,其水质的特征波动不同于淡水湖或海洋(McLusKY 1989)。在咸淡水地区,盐度随潮汐和淡水流量的变化有较大的波动,这对建立理化水质的分布和动态起着关键作用。盐度的波动影响生物种类的分布。当咸淡水中形成强烈的盐斜层时,上下水层之间物质的垂直混合受到限制(LouGEE et al. 2002, DEDA et al. 2005)。因此,咸淡湖的水质和生态系统的特征在上层和下层是不同的。位于日本六所所的小渊湖(Lake Obuchi)周围是一座核燃料再处理厂。少量的放射性核素(如Kr、H、C和I)从后处理工厂释放出来,可能通过潮汐从海洋进入这个湖,通过河流从陆地进入这个湖,通过沉降物从大气进入这个湖。这些放射性核素的行为受到湖泊生态系统环境因素的强烈影响。因此,必须对后处理工厂释放的放射性物质的影响进行评估,以评估周围环境的安全性,并为该湖建立放射性核素转移模型。我们开发了放射性核素转移模型,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等人,2006年);然而,浮游植物初级产量的计算精度略低。为了提高模型的可重复性,必须获得与野外浮游植物初级产量有关的参数。在本研究中,我们明确了小渊湖浮游植物初级产量的垂直分布和环境因子(如水质、水温、盐度和辐照度),以获得与野外初级产量相关的参数。此外,我们还利用C技术研究了光合作用与上层和下层辐照度(P-I曲线)曲线的关系。
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Relationships between primary production of phytoplankton and environmental factors in a shallow brackish lake
Brackish lakes and estuaries are strongly affected by both terrestrial and oceanic factors because ofthe complex mixing of fresh water and seawater, and their characteristic fluctuations in water quality differ from those o f 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 ofthe 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, DEDA et al. 2005). Therefore, water quality and characterization of an ecosystem in a brackish lake differ in its upper and lower layers. Brackish Lake Obuchi in Rokkasho, Japan, is bordered by a nuclear spent-fuel reprocessing plant. Small amounts of radionuclides (such as Kr, H, C, and 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. In this study we clarified the vertical distributions of primary production ofphytoplankton and environmental factors (such as water quality, water temperature, salinity, and irradiance) 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 C technique.
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