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Control of phosphorus distribution and regeneration in eutrophic systems.

机译:控制富营养化系统中磷的分布和再生。

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Mechanisms controlling the concentration, transport, and distribution of phosphorus in nutrient enriched environments were examined. Biological processes were hypothesized to control both organic phosphorus cycling and inorganic phosphorus chemistry. Soil profiles of phosphorus, nitrogen, and carbon delineated prehistoric archaeological site boundaries. Boundaries corresponded to organic phosphorus concentrations and artifact densities. Higher mobility and adsorption to metals made inorganic phosphorus a poor indicator. Temporal changes in qualitative and quantitative organic matter loading were indicated by changes in organic P:C ratios. Mass balance modeling of phosphorus, nitrogen and dissolved oxygen in the upper Charles River differed from traditional nutrient transport models both daily and seasonally. Observed phosphorus, nitrogen, and dissolved oxygen deficits were balanced by the addition of macrophyte dynamics, which contributed 30–85% of the ecosystem oxygen demand. Incorporation of phosphorus into macrophytes limited expression of oxygen demand during periods of historic hypoxia and contributed to improved water quality. Phosphorus and nitrogen distribution and iron cycling rates were determined in a permanently stratified, diffusion dominated antarctic lake. Iron reduction rates determined from diffusive flux and enzyme kinetics were used to model electron transfer through the metalimnion. Tight coupling of Fe and Mn cycling eliminated potential interactions affecting phosphorus distributions in other environments. Mass balance calculations confirmed short-term steady state conditions, long residence times, and low recycling rates, but were inconsistent with the hypothesized long-term stability of these systems. Water column and sediment phosphorus cycling relative to iron and manganese reduction and oxygen dynamics were examined further in a temperate lake receiving inputs of phosphorus and manganese. Modeling of nutrient and metal masses indicated a dominant sediment source responding to seasonal anoxia and a significant external source of manganese. High rates of biological manganese and iron reduction occurred throughout the metalimnion, where respiration was limited by organic carbon. Iron and manganese cycling was uncoupled by a large external input of manganese which was a critical control of phosphate and iron distribution. In each of the four environments microbial organic matter decomposition controlled organic phosphorus dynamics, while microbial respiration and mediation of trace metal interactions controlled inorganic phosphorus chemistry and distribution.
机译:研究了在营养丰富的环境中控制磷的浓度,迁移和分布的机制。假设生物过程可以控制有机磷循环和无机磷化学。磷,氮和碳的土壤剖面描绘了史前考古遗址的边界。边界对应于有机磷浓度和伪影密度。较高的迁移率和对金属的吸附使无机磷成为较差的指标。有机和有机碳比率的变化表明了有机质的定性和定量变化。查尔斯河上游的磷,氮和溶解氧的质量平衡模型在日常和季节性方面均不同于传统的养分迁移模型。观察到的磷,氮和溶解氧的缺乏通过增加大型植物的动力学来平衡,这贡献了生态系统需氧量的30–85%。在历史性缺氧期间,将磷掺入大型植物会限制氧气需求的表达,并有助于改善水质。在永久性分层,扩散为主的南极湖中测定了磷和氮的分布以及铁的循环速率。由扩散通量和酶动力学确定的铁还原率用于模拟通过金属酰亚胺的电子转移。铁和锰循环的紧密耦合消除了影响其他环境中磷分布的潜在相互作用。质量平衡计算证实了短期稳态条件,较长的停留时间和较低的回收率,但与这些系统的假定长期稳定性不一致。在接受磷和锰输入的温带湖泊中,进一步研究了水柱和沉积物磷相对于铁和锰还原以及氧气动力学的循环。营养物和金属质量的模型表明,主要的沉积物源对季节性缺氧有响应,而锰是重要的外部源。在整个金属酰亚胺中,生物锰和铁的还原率很高,而呼吸受有机碳限制。铁和锰的循环与大量外部锰输入无关,锰是磷酸盐和铁分布的关键控制因素。在这四种环境中,微生物有机物的分解均控制着有机磷的动力学,而微生物的呼吸作用和微量金属相互作用的介导则控制着无机磷的化学和分布。

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