Elsevier

Geochimica et Cosmochimica Acta

Volume 121, 15 November 2013, Pages 328-338
Geochimica et Cosmochimica Acta

Amino acid nitrogen isotopic composition patterns in lacustrine sedimenting matter

https://doi.org/10.1016/j.gca.2013.07.020Get rights and content

Abstract

Amino acids (AAs) comprise a large fraction of organic nitrogen (N) in plankton and sedimenting matter. Aquatic studies of organic N compounds in general and of AAs in particular, mostly concentrate on marine environments. In order to study the cycling and fate of organic N and AAs in lakes, we measured the N isotopic composition15N) of bulk organic matter (OM) and of single hydrolysable AAs in sediment trap and sediment samples from two Swiss lakes with contrasting trophic state: Lake Brienz, an oligotrophic lake with an oxic water column, and Lake Zug a eutrophic, meromictic lake. We also measured the N isotopic composition of water column nitrate, the likely inorganic N source during biosynthesis in both lakes. The δ15N–AA patterns found for the sediment trap material were consistent with published δ15N–AA data for marine plankton. The AA composition and primary δ15N–AA signatures are preserved until burial in the sediments. During early sedimentary diagenesis, the δ15N values of single AAs appear to increase, exceeding those of the bulk OM. This increase in δ15N–AA is paralleled by a decreased contribution of AAs to the total OM pool with progressed degradation, suggesting preferential AA degradation associated with a significant N isotope fractionation. Indicators for trophic level based on δ15N–AAs were determined, for the first time in lacustrine systems. In our samples, the trophic AAs were generally enriched in 15N compared to source AAs and higher trophic δ15N–AA values in Lake Zug were consistent with a higher trophic level of the bulk biomass compared to Lake Brienz. Especially the difference between average trophic δ15N–AAs and average source δ15N–AAs was sensitive to the trophic states of the two lakes. A proxy for total heterotrophic AA re-synthesis (ΣV), which is strongly associated with heterotrophic microbial reworking of the OM, was calculated based on δ15N values of trophic AAs. Higher ΣV in Lake Brienz indicate enhanced heterotrophic bacterial reworking of AAs under oligotrophic conditions. Despite changes in the δ15N–AA values within the sediments, the proxies based on these values were consistent over the studied sediment profile, indicating the preservation of trophic signatures; therefore, our results underscore that δ15N–AA analysis of sedimentary records represents a promising tool to assess trophic levels and bacterial re-synthesis in lakes.

Introduction

Nitrogen (N) is a major component of biomass and settling organic matter (OM). The availability of N controls autotrophic production and hence OM fluxes, both in marine and fresh water environments. To study the sources, biosynthesis, trophic transfer, and processing of OM, bulk δ15N measurements have been broadly applied in marine systems (e.g. Altabet et al., 1999, Peterson, 1999, Meador et al., 2007), estuaries (e.g. Middelburg and Nieuwenhuize, 1998), and lakes (Bernasconi et al., 1997, Hodell and Schelske, 1998, Lehmann et al., 2004a, Lehmann et al., 2004b, Kumar et al., 2011). Hydrolysable amino acids (AAs; abbreviation used throughout the manuscript for hydrolysable amino acids) comprise a large fraction of the organic N in phyto- and zooplankton, as well as sedimenting matter (Lee, 1988, Cowie and Hedges, 1992). Additional insights into food webs and the cycling of N can be gained by the stable isotope analysis of these vitally important compounds. For example, AA isotope measurements have been applied in studies on plankton food webs and feeding ecology in marine systems (McClelland and Montoya, 2002, McClelland et al., 2003, Loick et al., 2007, Popp et al., 2007, Hannides et al., 2009, Loick-Wilde et al., 2012), as well as terrestrial food webs and foraging habitats (e.g. Lorrain et al., 2009, Chikaraishi et al., 2011). δ15N–AA analysis of non-living marine OM were performed by McCarthy et al. (2007) and Calleja et al. (2013) with the goal to examine its source and processing history, and most recently, Sherwood et al. (2011) measured the δ15N–AA of modern and fossil gorgonian deep-sea corals to study the control for variable trophic processing and nitrate source partitioning.

The δ15N–AA approach is based upon differences in the organism-internal N isotopic fractionation, which occur during metabolic processes. Glutamic acid (Glu) becomes enriched in 15N during transamination and deamination reactions, associated with the cleavage of a carbon–nitrogen bond. In contrast, N isotopes are barely fractionated during the conversion of phenylanaline (Phe) to tyrosine (Tyr), since no carbon–nitrogen bond has to be cleaved or formed (Chikaraishi et al., 2007). McClelland and Montoya (2002) found that the δ15N of some AAs (e.g. Glu and aspartic acid (Asp)) consistently increases with every trophic transfer, while the δ15N of other AAs (e.g. Phe, serine (Ser), threonine (Thr)) remains basically unchanged. The AAs whose δ15N remain unchanged during trophic transfer thus provide unbiased information on the δ15N of the sources at the base of the food web (“source AAs”), while the so-called “trophic AAs”, which display systematic enrichment in 15N with each trophic transfer, represent indicators for the trophic history (McClelland and Montoya, 2002, McClelland et al., 2003). Moreover, an index that describes the degree of total AA re-synthesis due to heterotrophic microbial reworking of the detrital OM (ΣV) was introduced by McCarthy et al. (2007) and is calculated based on the average deviation of single δ15N values of trophic AAs with respect to the average δ15N value of trophic AAs in a sample.

Essentially all studies thus far making use of compound-specific N isotope measurements to investigate N sources and the fate of N containing OM in aquatic systems concentrate on marine environments. In this study, we tested the AA-based geochemical approaches with proven value in marine studies for the first time in lacustrine settings. We measured the δ15N of single hydrolysable AAs and bulk δ15N of sediment trap and sediment samples, as well as the bulk δ15N of suspended POM and zooplankton samples in two Swiss lakes with different trophic state in order to study changes in the AA isotopic composition of the particulate matter with degradation and bacterial reworking. Furthermore, we wanted to test if the proxies based on δ15N–AA for trophic levels applied on sedimenting OM can reveal trophic levels of the lakes and whether the values of these proxies change during early degradation. In addition, we measured the δ15N of nitrate (NO3) in the water column with the goal to trace biogeochemical N transformations in the water column and to gain information on the δ15N of the inorganic N which is most likely taken up by the phytoplankton at the base of the food web.

Section snippets

Sampling sites

Lake Brienz is a peri-alpine lake in the northern ranges of the Swiss Alps, with an oxic water column. The lake has a surface area of 29.8 km2 and a volume of 5.2 km3. The maximum depth of the lake is 259 m. The catchment is drained by the two main inflows, the Aare and the Lütschine, which together transport an annual average of 300,000 tons of suspended material into Lake Brienz (Anselmetti et al., 2007). In contrast to the particle load, the nutrient input is low, explaining the oligotrophic

Nitrate concentrations and isotopic composition

In Lake Brienz in spring, NO3 concentrations and δ15NO3 values were essentially invariant at 6.5 μmol L−1 and 1–2‰, respectively, throughout the water column (Fig. 1). By autumn, a subtle decrease in NO3 concentration to 4.8 μmol L−1 was observed in the surface waters, while in the hypolimnion the concentrations remained unchanged (Fig. 1). As in spring, δ15NO3 values were quite constant over the entire water column in autumn (0.6–1.8‰). In Lake Zug during the spring sampling, NO3

Acknowledgments

We are grateful to M. Schurter for help with sediment coring and the deployment of sediment traps. K. Köllner and T. Diem are gratefully acknowledged for plankton sampling. We would like to thank G. Nobbe whom we unfortunately lost from our lab due to severe illness for assistance in the lab. J. Bolotin is thanked for help with δ15N–AA analysis and R. Stierli for measuring NO3 concentrations. Many thanks to Dr. Y. Chikaraishi and an anonymous reviewer for their valuable and constructive

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