Fundamental and Applied Limnology / Archiv für Hydrobiologie · 2008 · 88 citations · 33 references
Life SciencesEcologyFreshwater EcologyNutrient CyclingPlankton EcologyAquatic Nutrient CyclingNitrogen NutritionNutrient DynamicsNutrient LimitationNutrient LoadingPhytoplankton EcologyExperimental Tank TestingLake Nutrient LoadingNitrate AccumulationNitrogen:phosphorus RatioNutrient Load ManagementPhytoplankton BiomassPhytoplankton Nutrient DynamicsPlant Species Abundance
Increased nitrogen loading may lead to changes in productivity or biodiversity in freshwater systems. Field surveys have shown reduced species richness of submerged and fl oating-leaved plant communities in shal- low lakes as winter nitrate concentrations, a surrogate for nitrate loading, have risen above 1-2 mg NO3-N L -1 . Experimental tank mesocosms, containing about 3 m 3 of water and sediment from Hickling Broad, Norfolk, UK were initially planted with eleven submerged plant species from the lake and its connected waterway. Constant phosphorus loadings (designed to give added concentrations of 50 µg P L -1 ) were given to all tanks. Four nitrate loadings were given in a randomised block design with twelve-fold replication. Loadings were designed to increase the concentration in the water by 1, 2, 5 and 10 mg NO3-N L -1 (N1, N2, N5 and N10, respectively). Nitrate loading increased phytoplankton and periphyton chlorophyll a in the N2, N5 and N10 treatments compared with the N1. It complementarily decreased total plant volume and had varied effects on different species, with most species indif- ferent, a few (mostly charophytes) declining above the N1 treatment, and one (Elodea canadensis) performing best in N2 and N5 compared with N1 and N10. Species richness of submerged macrophytes declined with time in all treatments and with increasing nitrogen load in the fi rst year. In the second year, species richness did not further decline in the N1 treatment but declined at increasing rates with increasing nitrogen load in the others. The rate of decline in the second year, plotted against nitrate load, fi tted an exponential relationship, allowing calculation of a critical load associated with a stable species richness of 0.61-0.64 mg NO3-NL -1 expressed as concentration in infl ow water, or of an empirically determined equivalent TN concentration in the lake water of about 1.50 mg N L -1 . This value broadly corresponds with estimates from fi eld data for concentrations associated with declining species richness and is much lower than values currently often found in lowland agricultural areas in Europe.
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HUMAN ALTERATION OF THE GLOBAL NITROGEN CYCLE: SOURCES AND CONSEQUENCES
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