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Landscape-scale patterns of nitrogen fixation by cyanobacteria

机译:蓝细菌固氮的景观尺度格局

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Cyanobacteria blooms are characteristic of eutrophic lakes and are often a threat to water consumption (Millie et al. 1999). Lakes of the prairie ecozone of Canada are particularly prone to cyanobacteria blooms harbouring nitrogen-fixers (Aphanizomenon, Anabaena, Gloeotrichia spp.), in part because of phosphorus (P)-rich soils and high irradiance regimes (Barica 1987). However, despite the prevalence of cyanobacteria in phytoplankton of some lakes, there is little agreement on whether nitrogen fixed from the atmosphere (N_2) is quantitatively incorporated into the aquatic food web. On one hand, their colonial nature and potential toxicity make het-erocystous cyanobacteria poor food for zooplankton (Ghadouani et al. 2004). On the other hand, historical correlations between cyanobacterial abundance and stable isotope signals in plankton and lake sediments (Talbot 2001) suggest that atmospheric N2 fixed by cyanobacteria may be an important source of nitrogen (N) to lake ecosystems. Little is known of how the importance of N sources may vary as a function of lake position within the greater landscape. Many chemical properties of lakes are strongly influenced by the position of a lake within the hydrologic or topographic landscape, such that headwater lakes tend to exhibit lower nutrient concentrations and algal densities than do downstream sites (Soranno et al. 1999). Based on these patterns, we hypothesized that the intensity of N_2 fixation by cyanobacteria should increase with distance from headwaters, and that fixed N_2 should be more completely incorporated into the primary and secondary consumers of downstream lakes.
机译:蓝藻水华是富营养化湖泊的特征,通常是对水消耗的威胁(Millie等,1999)。加拿大大草原生态区的湖泊特别容易产生带有固氮剂的蓝藻水华(Aphanizomenon,Anabaena,Gloeotrichia spp。),部分原因是富含磷(P)的土壤和高辐照度制度(Barica 1987)。然而,尽管某些湖泊的浮游植物中普遍存在蓝细菌,但对于从大气中固定的氮(N_2)是否被定量地掺入水生食物网中,尚无共识。一方面,它们的殖民性质和潜在毒性使异养藻蓝藻成为浮游动物的不良食物(Ghadouani等,2004)。另一方面,浮游生物和湖泊沉积物中的蓝细菌丰度与稳定同位素信号之间的历史相关性(Talbot 2001)表明,蓝​​细菌固定的大气氮可能是湖泊生态系统中氮的重要来源。人们对于氮源的重要性如何随更大景观中湖泊位置的变化而知之甚少。湖泊的许多化学性质受到湖泊在水文或地形景观中的位置的强烈影响,因此源头湖泊往往比下游地区表现出更低的养分浓度和藻类密度(Soranno等人,1999)。基于这些模式,我们假设蓝藻对N_2的固定强度应随距源头距离的增加而增加,并且固定N_2应更完全地纳入下游湖泊的主要和次要消费者中。

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