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Development and persistence of deep chlorophyll maxima in oligotrophic lakes over the summer season

机译:夏季贫营养湖中深层叶绿素最大值的形成和持久性

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摘要

Deep chlorophyll maxima (DCM) are common features in temperate and tropical oligo-mesotrophic stratified lakes, where they can account for an important part of the primary production (Fee 1976, Cullen 1982, Pick et al. 1984, Pedros-Alio et al. 1987, Padisak et al. 2003). However, the mechanisms that lead to the development and persistence of DCMs remain to be fully understood (Perez et al. 2002, Burnett et al. 2006, Sawatzky et al. 2006). A number of hypotheses have been proposed to explain the development and persistence of DCMs in lakes: (1) the limiting resource hypothesis, stating that DCM is due to in situ algal productivity in the metalimnion, where nutrient supply comes from mineralisation of sinking epilimnetic particles and zooplankton excretion (Carmacho et al. 2000); (2) the behavioural hypothesis, stating that only mobile or mixotrophic algae species adapted to low light develop in DCM layers (Fahnenstiel & Glime 1983, Pedros-Alio et al. 1987); (3) the sedimentation hypothesis, stating that sinking of epilimnetic algae over depth along the density gradient generates DCM in the metalimnion (Cullen 1982); and (4) the depth-specific zooplankton grazing hypothesis, stating that lower grazing rate in the metalimnion lead to the maintenance of DCM (Pilati & Wurtsbaugh 2003). In fact, several of these processes may interact to control the development and persistence of DCMs in lakes (Richerson et al. 1978, Padisak et al. 2003, Burnett et al. 2006). We describe the development and persistence of DCMs using high resolution in situ fluorometry in 3 Laurentian lakes (Quebec, Canada) during summer 2002. The objective of this study was to evaluate how DCM patterns were related to environmental factors such as photosynthetic active radiation, nutrients, and crustacean zooplankton community.
机译:深温叶绿素最大值(DCM)是温带和热带中亚营养型分层湖泊中的常见特征,它们可以占初级生产的重要部分(Fee 1976,Cullen 1982,Pick等人1984,Pedros-Alio等人。 1987年,Padisak等人,2003年)。但是,导致DCM发生和持久化的机制仍有待充分了解(Perez等,2002; Burnett等,2006; Sawatzky等,2006)。提出了许多假设来解释DCM在湖泊中的发展和持久性:(1)有限的资源假设,指出DCM是由于金属酰亚胺中的原位藻类生产力所致,其中养分供应来自沉没的表皮磁性颗粒的矿化作用。和浮游动物的排泄(Carmacho等人,2000年); (2)行为假说,指出DCM层中仅发育适应弱光的流动或混养藻类(Fahnenstiel&Glime 1983,Pedros-Alio等人,1987); (3)沉积假说,表明沿密度梯度在深度上表生藻类的下沉会在金属酰亚胺中产生DCM(Cullen 1982); (4)深度特定的浮游动物放牧假说,指出金属酰亚胺中较低的放牧率导致维持DCM(Pilati&Wurtsbaugh 2003)。实际上,这些过程中的一些过程可能相互作用,以控制DCM在湖泊中的发育和持久性(Richerson等,1978; Padisak等,2003; Burnett等,2006)。我们描述了2002年夏季在3个Laurentian湖(加拿大魁北克)中使用高分辨率原位荧光法描述DCM的发展和持久性。本研究的目的是评估DCM模式与环境因素(如光合作用的活性辐射,养分)如何相关,以及甲壳类浮游动物群落。

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