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Die Charakterisierung und Quantifizierung von Phytoplankton-Gemeinschaften sind ein wesentlicher Aspekt der Gütebeurteilung von Standgewässern. In dieser Arbeit wird eine neue Herangehensweise hergeleitet und demonstriert, welche die klassische, taxonomisch-orientierte Methodik durch einen funktionalen Ansatz ergänzt, der auf den physiologischen und ökologischen Eigenschaften der Taxa (Traits) beruht. Kern des Ansatzes bildet der sogenannte Trait-Schlüssel, mit dem eine taxonomische Information in eine funktionale Information übersetzt werden kann. Die Aussagekraft und Potenziale des Verfahrens werden anhand von Langzeitdaten (50 Jahre) der Phytoplankton-Gemeinschaft der Rappbode-Talsperre exemplarisch demonstriert. Die Trait-basierte Analyse reduziert die Komplexität der Daten und ermöglicht eine quantitative Analyse der beobachteten Veränderungen auf der Basis von statistischen Methoden, die auf den klassischen taxonomischen Ansatz nicht anwendbar sind. Sowohl hinsichtlich der saisonalen Sukzession als auch der langfristigen Trends lassen die funktionalen Eigenschaften Rückschlüsse auf die maßgeblichen Umweltfaktoren zu. Für die wasserwirtschaftliche Praxis erweitert sich damit der Informationsgehalt und die Interpretierbarkeit der vorhandenen Daten. Diese Aufwertung der Ergebnisse kann ohne Mehraufwand erhalten werden. Von besonderem Interesse sind hierbei Kausalanalysen signifikanter Langzeittrends oder von sprunghaften Veränderungen in der Phytoplankton-Entwicklung, die hiermit in einen kausalen und systemanalytischen Zusammenhang gestellt werden können.
Meeting ecological and water quality standards in lotic ecosystems is often failed due to multiple stressors. However, disentangling stressor effects and identifying relevant stressor-effect-relationships in complex environmental settings remain major challenges. By combining state-of-the-art methods from ecotoxicology and aquatic ecosystem analysis, we aimed here to disentangle the effects of multiple chemical and non-chemical stressors along a longitudinal land use gradient in a third-order river in Germany. We distinguished and evaluated four dominant stressor categories along this gradient: (1) Hydromorphological alterations: Flow diversity and substrate diversity correlated with the EU-Water Framework Directive based indicators for the quality element macroinvertebrates, which deteriorated at the transition from near-natural reference sites to urban sites. (2) Elevated nutrient levels and eutrophication: Low to moderate nutrient concentrations together with complete canopy cover at the reference sites correlated with low densities of benthic algae (biofilms). We found no more systematic relation of algal density with nutrient concentrations at the downstream sites, suggesting that limiting concentrations are exceeded already at moderate nutrient concentrations and reduced shading by riparian vegetation. (3) Elevated organic matter levels: Wastewater treatment plants (WWTP) and stormwater drainage systems were the primary sources of bioavailable dissolved organic carbon. Consequently, planktonic bacterial production and especially extracellular enzyme activity increased downstream of those effluents showing local peaks. (4) Micropollutants and toxicity-related stress: WWTPs were the predominant source of toxic stress, resulting in a rapid increase of the toxicity for invertebrates and algae with only one order of magnitude below the acute toxic levels. This toxicity correlates negatively with the contribution of invertebrate species being sensitive towards pesticides (SPEARpesticides index), probably contributing to the loss of biodiversity recorded in response to WWTP effluents. Our longitudinal approach highlights the potential of coordinated community efforts in supplementing established monitoring methods to tackle the complex phenomenon of multiple stress.
We employed the well-established Horton-Strahler, hierarchical, stream-order (ω) scheme to investigate scaling of nutrient loads (P and N) from ~845 wastewater treatment plants (WWTPs) distributed along the river network in urbanized Weser River, the largest national basin in Germany (~46K km2; ~8.4 million population). We estimated hydrologic and water quality impacts at the reach- and basin-scales, at two steady river discharge conditions (median flow, QR50; low-flow, QR90). Of the five WWTPs class-sizes (1 ≤ k ≤ 5), ~68% discharge to small low-order streams (ω < 3). We found large variations in capacity to dilute WWTP nutrient loads because of variability in (1) treated wastewater discharge (QU) within and among different class-sizes, and (2) river discharge (QR) within low-order streams (ω < 3) resulting from differences in drainage areas. For QR50, reach-scale water quality impairment assessed by nutrient concentration was likely at 136 (~16%) locations for P and 15 locations (~2%) for N. About 90% of these locations were lower-order streams (ω < 3). At QR50 and only with dilution, basin-scale cumulative nutrient loads from multiple upstream WWTPs increase impaired locations to 266 (~32% of total) for P. Considering in-stream uptake decreased P-impaired streams to 225 (~27%), suggesting the dominant role of dilution in the Weser River basin. Role of in-stream uptake diminished along the flow paths, while dilution in larger streams (4 ≤ ω ≤ 7) minimizes the impact of WWTP loads. Under QR90 conditions [(QR50/QR90) ~ 2.5], water quality impaired locations will likely double for the basin-scale analyses. Long-term water quality data suggested that diffuse sources are the primary contributors for water quality impairments in large streams. Our data-modeling synthesis approach is transferable to other urbanized river basins and extends understanding of point source impacts on water quality across spatial scales.