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Effects of upstream lakes and nutrient limitation on periphytic biomass and nitrogen fixation in oligotrophic, subalpine streams

机译:上游湖泊和养分限制对贫营养性亚高山流水生植物生物量和固氮的影响

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1. We conducted bioassays of nutrient limitation to understand how macronutrients and the position of streams relative to lakes control nitrogen (N) fixation and periphytic biomass in three oligotrophic Rocky Mountain catchments. We measured periphytic chlorophyll-a (chl-a) and nitrogen-fixation responses to nitrogen (N) and phosphorus (P) additions using nutrient-diffusing substrata at 19 stream study sites, located above and below lakes within the study catchments. 2. We found that periphytic chl-a was significantly co-limited by N and P at 13 of the 19 sites, with sole limitation by P observed at another four sites, and no nutrient response at the final two sites. On average, the addition of N, P and N + P stimulated chl-a 35%, 114% and 700% above control values respectively. The addition of P alone stimulated nitrogen fixation by 2500% at five of the 19 sites. The addition of N, either with or without simultaneous P addition, suppressed nitrogen fixation by 73% at nine of the 19 sites. 3. Lake outlet streams were warmer and had higher dissolved organic carbon concentrations than inlet streams and those further upstream, but position relative to lakes did not affect chl-a and nitrogen fixation in the absence of nutrient additions. Chl-a response to nutrient additions did not change along the length of the study streams, but nitrogen fixation was suppressed more strongly by N, and stimulated more strongly by P, at lower altitude sites. The responses of chl-a and nitrogen fixation to nutrients were not affected by location relative to lakes. Some variation in responses to nutrients could be explained by nitrate and/or total N concentration. 4. Periphytic chl-a and nitrogen fixation were affected by nutrient supply, but responses to nutrients were independent of stream position in the landscape relative to lakes. Understanding interactions between nutrient supply, nitrogen fixation and chl-a may help predict periphytic responses to future perturbations of oligotrophic streams, such as the deposition of atmospheric N.
机译:1.我们进行了养分限制的生物测定,以了解宏观营养素和河流相对于湖泊的位置如何控制三个贫营养落基山流域的固氮和周围生物量。我们使用位于研究集水区湖泊上方和下方的19个溪流研究地点的营养扩散基质测量了周围植物的叶绿素a(chl-a)和固氮对添加的氮(N)和磷(P)的响应。 2.我们发现,在19个位点中的13个位点,植物周围的chl-a受N和P显着共限,在另外四个位点仅受P限制,在最后两个位点无养分响应。平均而言,N,P和N + P的添加分别刺激chl-a比对照值高35%,114%和700%。在19个位点中的五个位点上,单独添加P可以使固氮率提高2500%。在19个位点中的9个位点上,无论是否同时添加P,添加N都会使固氮率降低73%。 3.湖泊出口溪流比入口河流和上游溪流更热,并具有更高的溶解有机碳浓度,但是在没有添加营养物的情况下,相对于湖泊的位置不会影响chl-a和固氮。 Chl-a对营养添加的响应在研究流的长度上没有变化,但是在较低海拔的地点,固氮被N抑制得更强烈,而P则刺激更强烈。相对于湖泊的位置,chl-a和固氮对养分的响应不受位置的影响。硝酸盐和/或总氮浓度可以解释对养分响应的某些变化。 4.养分的供应源影响了周围生植物的chl-a和固氮作用,但是对养分的响应与景观相对于湖泊的水流位置无关。了解养分供应,固氮和chl-a之间的相互作用可能有助于预测对营养不足流的未来扰动(例如大气氮的沉积)的周生响应。

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