Laverman Anniet M, Canavan Richard W, Slomp Caroline P, Cappellen Philippe Van
Department of Earth Sciences-Geochemistry, Faculty of Geosciences, Utrecht University, P.O. Box 80021, 3508 TA Utrecht, The Netherlands.
Water Res. 2007 Jul;41(14):3061-8. doi: 10.1016/j.watres.2007.04.002. Epub 2007 Jun 4.
Nitrogen transformations and their response to salinization were studied in bottom sediment of a coastal freshwater lake (Haringvliet Lake, The Netherlands). The lake was formed as the result of a river impoundment along the south-western coast of the Netherlands, and is currently targeted for restoration of estuarine conditions. Nitrate porewater profiles indicate complete removal of NO(3)(-) within the upper few millimeters of sediment. Rapid NO(3)(-) consumption is consistent with the high potential rates of nitrate reduction (up to 200 nmol N cm(-3) h(-1)) measured with flow-through reactors (FTRs) on intact sediment slices. Acetylene-block FTR experiments indicate that complete denitrification accounts for approximately half of the nitrate reducing activity. The remaining NO(3)(-) reduction is due to incomplete denitrification and alternative reaction pathways, most likely dissimilatory nitrate reduction to NH(4)(+) (DNRA). Results of FTR experiments further indicate that increasing bottom water salinity may lead to a transient release of NH(4)(+) and dissolved organic carbon from the sediment, and enhance the rates of nitrate reduction and nitrite production. Increased salinity may thus, at least temporarily, increase the efflux of NH(4)(+) from the sediment to the surface water. This work shows that salinity affects the relative importance of denitrification compared to alternative nitrate reduction pathways, limiting the ability of denitrification to remove bioavailable nitrogen from aquatic ecosystems.
在荷兰沿海淡水湖(哈灵弗利特湖)的底部沉积物中研究了氮转化及其对盐渍化的响应。该湖是荷兰西南海岸河流蓄水形成的,目前的目标是恢复河口环境。硝酸盐孔隙水剖面表明,在沉积物上部几毫米内,NO(3)(-)被完全去除。快速的NO(3)(-)消耗与用流通式反应器(FTR)在完整沉积物切片上测得的高硝酸盐还原速率(高达200 nmol N cm(-3) h(-1))一致。乙炔抑制FTR实验表明,完全反硝化约占硝酸盐还原活性的一半。其余的NO(3)(-)还原是由于不完全反硝化和替代反应途径,最有可能是异化硝酸盐还原为NH(4)(+)(DNRA)。FTR实验结果进一步表明,增加底层水盐度可能导致沉积物中NH(4)(+)和溶解有机碳的瞬时释放,并提高硝酸盐还原和亚硝酸盐产生速率。因此,盐度增加可能至少暂时增加沉积物中NH(4)(+)向地表水的流出。这项工作表明,与替代硝酸盐还原途径相比,盐度会影响反硝化的相对重要性,限制反硝化从水生生态系统中去除生物可利用氮的能力。