Christian K. Feld’s research while affiliated with University of Duisburg-Essen and other places

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Publications (3)


A Proof‐of‐Principle Study for δ 15 N Measurements of Aqueous Dissolved Nitrate With a Modified LC‐IRMS Interface
  • Article

November 2024

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34 Reads

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1 Citation

Rapid Communications in Mass Spectrometry

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Rationale The analysis of nitrogen isotopes in aqueous dissolved nitrate is an effective method for identifying pollution sources and offers the potential to study the nitrogen cycle. However, the measurement of nitrogen isotope ratios of nitrate still requires extensive sample preparation or derivatization. Methods In this study, a modified commercially available liquid chromatography–isotope ratio mass spectrometer (LC‐IRMS) interface is presented that enables automated measurement of δ ¹⁵ N signatures from nitrate by online reduction of nitrate in two consecutive steps. First, vanadium(III) chloride is used as a reducing agent to convert NO 3 ⁻ to N x O y under acidic conditions. The mix of nitrogen oxides is then transferred into a stream of helium and reduced to nitrogen (N 2 ) analysis gas via a hot copper reactor. Prior to the online conversion of aqueous nitrate into elemental nitrogen, the sample was chromatographically separated from potential matrix effects on a PGC column. Results Precision was achieved at a level below 1.4‰ by injecting 10 μL of 50 mg L ⁻¹ N, using five different nitrate standards and reference materials. These materials spanned a range of more than 180‰ in δ ¹⁵ N. To demonstrate the applicability of the method, we measured water samples from an enrichment experiment, where isotopically enriched ammonium chloride was administered into a small river over the course of 2 weeks. In contrary to our expectation, the δ ¹⁵ N values of river nitrate showed values between +0.4 ± 0.4‰ and +4.1 ± 0.3‰, varying over a small range of 3.7‰. Conclusions Our study showed that the measurement of nitrate nitrogen isotope ratios with a modified LC‐IRMS system is possible but that further modifications and improvements would be necessary for a robust and user‐friendly instrument.


Fig. 1. Location of sampling sites in the Federal States of Schleswig-Holstein (SH), North Rhine-Westphalia (NRW), Saxony (SN) and Bavaria (BY), Germany. Background colors indicate lowland regions (in green, altitude <200 m a.s.l.) and mountainous regions (in brown, altitude 200-800 m a.s.l.). No alpine sites at altitudes >800 m a.s.l. were sampled. ©GeoBasis-DE/BKG 2023.
Fig. 2. Distribution of explained variances of biological metrics in Random Forests (RF). Results for the initial selection of 56 candidate metrics (C) are shown in grey and for the final selection of 35 metrics (i.e., metrics with an explained variance equal to or larger than 15 % in the RF models, S) in black.
Fig. 3. Relative influence (%) of physical water quality stressors (PHY), salt ions (SALT), nutrients (NUT), micropollutant mixture toxicity (TOX), hydrological alteration (HYD) and morphological habitat degradation (HAB) in Random Forest (RF) models on macroinvertebrate (top), diatom (middle) and fish (bottom) community metrics. Explained variance (%) of RF models and metric classification (WQ = Water Quality, HQ = Habitat Quality, D = Richness/Diversity, F = Function, I = Integrating) are provided in parentheses behind metric codes. For full metric names, see Table 2.
Water quality deterioration remains a major stressor for macroinvertebrate, diatom and fish communities in German rivers
  • Article
  • Full-text available

October 2023

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366 Reads

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11 Citations

The Science of The Total Environment

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Sampling sites in the catchments of the river Erft and Niers. Sampling sites are located in the river Erft (dots) and the river Niers (triangles) in North Rhine-Westphalia (NRW), western Germany. Map colour corresponds to the elevation profile with green colours indicating lowlands and brown colours indicating low mountain ranges (artificial minimum of -299 m in mining area, natural range 9 m to 843 m above sea level). Colour of sampling sites show the stream types according to the German river typology for the EU WFD [43, 44] (©Data licence Germany-Zero-Version 2.0)
Principal component analyses biplot of all stressor variables. Sampling sites (dots) are colour-coded according to their Ecological Quality Class (EQC), with enlarged dots indicating the centroid for each EQC. For abbreviations of stressor variables, see Table 1
Venn diagram of the variance in macroinvertebrate metrics. Numbers indicate the unique and shared portions (adjusted R²) of the variance in 21 macroinvertebrate metrics (Table 2) that are explained by physico-chemistry, micropollutants, morphological degradation and hydrological alteration. R² values below zero are not shown
Selection of 21 benthic macroinvertebrate metrics included in the redundancy analysis and subsequent variance partitioning
The hierarchy of multiple stressors’ effects on benthic invertebrates: a case study from the rivers Erft and Niers, Germany

October 2022

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309 Reads

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12 Citations

Environmental Sciences Europe

Background A variety of anthropogenic stressors influences the ecological status of rivers wordwide. Important stressors include elevated concentrations of nutrients, salt ions, heavy metals and other pollutants, habitat degradation and flow alteration. Some stressors tend to remain underrepresented in multiple-stressor studies, which in particular is apparent for micropollutants (e.g. pesticides, pharmaceuticals) and alterations of the flow regime. This case study analysed and compared the effects of 19 different stressor variables on benthic macroinvertebrates in the two German rivers Erft and Niers (Federal State of North Rhine-Westphalia, Germany). The stressors variables were assigned to four stressor groups (physico-chemical stress, mixture toxicity of 42 micropollutants, hydrological alteration and morphological degradation) and were put into a hierarchical context according to their relative impact on the macroinvertebrate community using redundancy analysis and subsequent variance partitioning. Results The results suggest a strong and unique effect of physico-chemical stress, yet at the same time reveal also a strong joint effect of physico-chemical and hydrological stressor variables. Morphological degradation showed subordinate effects. Notably, only a minor share of the explained variance was attributed to the mixture toxicity of micropollutants in these specific catchments. Conclusions The stressor hierarchy indicates that management measures for improving the ecological status still need to address water quality issues in both rivers. The strong joint effect of physico-chemical stress and hydrological alteration might imply a common source of both stressor groups in these two catchment areas: lignite mining drainage, urban area and effluents of wastewater treatment plants. The findings point at the important role of alterations in the flow regime, which often remain unconsidered in hydro-morphological surveys.

Citations (3)


... The mix of nitrogen oxides is then transferred trough a membrane into a helium stream and reduced to nitrogen (N 2 ) analysis gas via a hot copper reactor. To adapt this method for the nitrogen isotope measurement of organic compounds, different adaptations are necessary [29]. ...

Reference:

Alkaline persulfate oxidation as an intermediate step for the development of a wet chemical oxidation interface for compound-specific δ15N analysis by LC-IRMS
A Proof‐of‐Principle Study for δ 15 N Measurements of Aqueous Dissolved Nitrate With a Modified LC‐IRMS Interface
  • Citing Article
  • November 2024

Rapid Communications in Mass Spectrometry

... Water quality deterioration is one of the most pressing threats to freshwater ecosystems, driven largely by rapid urbanization and intensive agricultural and industrial activities (Markert et al., 2024;Woodward et al., 2012). The influx of nutrients, organic matter, and chemical contaminants into rivers can lead to eutrophication and degradation of aquatic habitats, which in turn alters biotic community structure and disrupts trophic interactions (Allan, 2004;Cooper, 1993;Dodds, 2007). ...

Water quality deterioration remains a major stressor for macroinvertebrate, diatom and fish communities in German rivers

The Science of The Total Environment

... Since the 1990s, some scholars have begun to pay attention to factors at a larger scale, believing that landscape-scale and watershed-scale factors play an important role in the riverine macrobenthos macroinvertebrate community [15]. Currently, most scholars believe that riverine biodiversity is influenced by multi-scale, multitype factors, and research is focused on the effects of the coupling of multiple environmental factors on the community [9,16]. ...

The hierarchy of multiple stressors’ effects on benthic invertebrates: a case study from the rivers Erft and Niers, Germany

Environmental Sciences Europe