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Ecophysiological linkage of nitrogen enrichment to heavily silicified diatoms in winter

机译:冬季富氮与严重硅化硅藻的生态生理联系

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Over recent decades, increased anthropogenic nitrogen and reduced land-based loading of silica in many coastal waters have asymmetrically changed the nitrogen: silica ratios. These changes have contributed to shifts in phytoplankton assemblages from diatoms to non-diatoms, as well as increases in the frequency and magnitude of non-diatom harmful algal blooms. Here we show a subtle and counterintuitive change in diatom assemblage, i.e. heavily silicified diatoms significantly increased in winter after nitrogen enrichment, based on paleoecological and contemporary seasonal water column data from 2 eutrophic bays in the Yellow Sea. The heavily silicified diatom Paralia sulcata showed an increasing trend over time in parallel with nitrogen enrichment, which was associated with low temperature, and low dissolved inorganic nitrogen: phosphorus, high dissolved nitrogen: silica, and low ammonium: nitrate ratios on a seasonal basis. Applying recent insights regarding diatom nitrogen metabolism and its putative urea cycle, a physiological mechanism linking nitrogen, carbon, and silica metabolism is suggested to explain the phenomenon of increased silicification under winter conditions at the cellular level. Winter sequestration of silica in P. sulcata valves also has biogeochemical consequences, including a weakening of the silica pump and a slowing of biogenic silica dissolution, thereby reducing the availability of silica for further diatom growth in subsequent seasons and increasing the window of opportunity for summer growth of non-diatom harmful algal bloom species.
机译:在最近的几十年中,许多沿海水域中人为氮的增加和陆基二氧化硅的减少降低了氮与二氧化硅的比例。这些变化促使浮游植物的集合从硅藻转变为非硅藻,并且增加了非硅藻有害藻华的频率和强度。根据黄海2个富营养化海湾的古生态学和当代季节性水柱数据,在这里我们显示了硅藻组合的微妙和违反直觉的变化,即在富氮后冬季硅化硅藻含量显着增加。硅化程度高的硅藻Paralia sulcata随时间的推移显示出增加的趋势,同时伴随着氮的富集,这与低温,低溶解无机氮:磷,高溶解氮:二氧化硅和季节性铵:硝酸盐比率低有关。应用有关硅藻氮代谢及其假定的尿素循环的最新见解,提出了一种将氮,碳和二氧化硅代谢联系起来的生理机制,以解释在冬季条件下细胞水平硅化增加的现象。冬季在P. sulcata阀门中隔离二氧化硅也具有生物地球化学后果,包括二氧化硅泵的减弱和生物二氧化硅的溶解减慢,从而减少了二氧化硅在后续季节中进一步用于硅藻生长的可利用性,并增加了夏季的机会窗口非硅藻有害藻华物种的生长。

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