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A stable isotope tracer study of the influences of adjacent land use and riparian condition on fates of nitrate in streams.

机译:一项稳定的同位素示踪研究,用于研究邻近土地利用和河岸条件对溪流中硝酸盐命运的影响。

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The influence of land use on potential fates of nitrate (NO3-) in stream ecosystems, ranging from denitrification to storage in organic matter, has not been documented extensively. Here, we describe the Pacific Northwest component of Lotic Intersite Nitrogen eXperiment, phase II (LINX II) to examine how land-use setting influences fates of NO3- in streams. We used 24 h releases of a stable isotope tracer (15NO3-N) in nine streams flowing through forest, agricultural, and urban land uses to quantify NO3 - uptake processes. NO3 - uptake lengths varied two orders of magnitude (24-4247 m), with uptake rates (6.5-158.1 mg NO3-N m-2 day-1) and uptake velocities (0.1-2.3 mm min-1) falling within the ranges measured in other LINX II regions. Denitrification removed 0-7% of added tracer from our streams. In forest streams, 60.4 to 77.0% of the isotope tracer was exported downstream as NO3-, with 8.0 to 14.8% stored in wood biofilms, epilithon, fine benthic organic matter, and bryophytes. Agricultural and urban streams with streamside forest buffers displayed hydrologic export and organic matter storage of tracer similar to those measured in forest streams. In agricultural and urban streams with a partial or no riparian buffer, less than 1 to 75% of the tracer was exported downstream; much of the remainder was taken up and stored in autotrophic organic matter components with short N turnover times. Our findings suggest restoration and maintenance of riparian forests can help re-establish the natural range of NO3- uptake processes in human-altered streams.
机译:从反硝化到有机物存储,土地利用对河流生态系统中硝酸盐(NO 3 -)的潜在命运的影响尚未得到广泛记录。在这里,我们描述了Lotic II位氮素试验第二阶段(LINX II)的西北太平洋成分,以研究土地利用环境如何影响河流中NO 3 -的命运。我们在流经森林,农业和城市土地的九种溪流中使用了24小时释放的稳定同位素示踪剂( 15 NO 3 -N)来定量NO 3 -摄取过程。 NO 3 -的吸收长度变化了两个数量级(24-4247 m),吸收速率(6.5-158.1 mg NO 3 -N) m -2 天 -1 )和摄取速度(0.1-2.3 mm min -1 )在其他LINX II地区测得的范围内。反硝化作用从流中去除了0-7%的添加示踪剂。在森林溪流中,同位素示踪剂的60.4%至77.0%作为NO 3 -出口到下游,其中8.0%至14.8%存储在木质生物膜,表石,精细底栖有机物中和苔藓植物。具有河流旁森林缓冲带的农业和城市河流显示出的水文出口量和示踪剂的有机物存储量与森林河流中测得的相似。在部分或没有河岸缓冲带的农业和城市河流中,只有不到1%到75%的示踪剂出口到下游。剩余的大部分被吸收并以短的N周转时间存储在自养有机物质组分中。我们的发现表明,河岸带森林的恢复和维护可以帮助重新建立人类改变流中NO 3 -吸收过程的自然范围。

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