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Biogeochemical processes at the sediment-water interface, Bombah Broadwater, Myall Lakes

机译:密巴拉湖Bombah Broadwater沉积物-水界面的生物地球化学过程

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Myall Lakes has experienced algal blooms in recent years which threaten water quality. Biomarkers, benthic fluxes measured with chambers, and pore water metabolites were used to identify the nature and reactivity of organic matter (OM) in the sediments of Bombah Broadwater (BB), and the processes controlling sediment-nutrient release into the overlying waters. The OM in the sediments was principally from algal sources although terrestrial OM was found near the Myall River. Terrestrial faecal matter was identified in muddy sediments and was probably sourced via runoff from farm lands. The reactive OM which released nutrients into the overlying waters was from diatoms, dinoflagellates and probably cyanobacteria. Microcystis filaments were observed in surface sediments. OM degradation rates varied between 5.3 and 47.1 mmol mpo dayp# (64-565 mg mpo dayp#), were highest in the muddy sediments and sulphate reduction rates accounted for 20-40% of the OM degraded. Diatoms, being heavy sink rapidly, and are an important vector to transport catchment N and P to sites of denitrification and P-trapping in the sediments. Denitrification rates (mean ~4 mmol N mpo dayp#), up to 7 mmol N mpo dayp# (105 mg N mpo dayp#) were measured, and denitrification efficiencies were highest (mean = 86 pl 4%) in the sandy sediments (~20% of the area of BB), but lower in the muddy sediments (mean = 63 pl 15%). These differences probably result from higher OM loads and anaerobic respiration in muddy sediments. Most DIP (>70%) from OM degradation was not released into overlying waters but remained trapped in surface sediments. Biophysical (advective) processes were responsible for the measured metabolite (O, CO, DSi, DIN and DIP) fluxes across the sediment-water interface.
机译:迈尔湖(Myall Lakes)近年来经历了藻华,威胁着水质。使用生物标志物,通过腔室测量的底栖通量和孔隙水代谢产物来确定Bombah Broadwater(BB)沉积物中有机物(OM)的性质和反应性,以及控制沉积物-养分释放到上层水体中的过程。尽管在Myall河附近发现了地面OM,但沉积物中的OM主要来自藻类。在泥泞的沉积物中发现了陆生粪便,很可能是通过农田的径流而来的。将营养释放到上层水中的反应性OM来自硅藻,鞭毛藻和可能是蓝细菌。在表面沉积物中观察到微囊藻丝。 OM降解速率在5.3至47.1 mmol mpo dayp#(64-565 mg mpo dayp#)之间变化,在泥泞的沉积物中最高,硫酸盐还原率占OM降解的20-40%。硅藻沉重迅速,是将集水区N和P输送到沉积物中反硝化和P捕集的重要载体。测量了沙质沉积物中的反硝化率(平均〜4 mmol N mpo·dayp#),最高7 mmol N mpo·dayp#(105 mg N mpo·dayp#),反硝化效率最高(平均值= 86 pl 4%)。约占BB面积的20%),但在泥泞的沉积物中含量较低(平均值= 63 pl 15%)。这些差异可能是由于较高的OM负荷和泥沙中的厌氧呼吸所致。 OM降解引起的大多数DIP(> 70%)没有释放到上覆水中,但仍被困在表层沉积物中。生物物理(对流)过程是通过沉积物-水界面的代谢物(O,CO,DSi,DIN和DIP)通量的原因。

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