Abstract

Lake sediments provide excellent archives to study past environmental and hydrological changes at high temporal resolution. However, their utility is often restricted by chronological uncertainties due to the “reservoir age effect” (RAE), a phenomenon that results in anomalously old radiocarbon ages of total organic carbon (TOC) samples that is mainly attributed to the contribution of pre-aged carbon from aquatic organisms. Although the RAE is a well-known problem especially in high altitude lakes, detailed studies analyzing the temporal variations in the contribution of terrestrial and aquatic organic carbon (OC) on the RAE are scarce. This is partially due to the complexity of isolating individual compounds for subsequent compound-specific radiocarbon analysis (CSRA). We developed a rapid method for isolating individual short-chain (C16and C18) and long-chain (>C24) saturated fatty acid methyl esters (FAMEs) by using high-pressure liquid chromatography (HPLC). Our method introduces only minor contaminations (0.50 ± 0.22 µg dead carbon on average) and requires only few injections (≤10), therefore offering clear advantages over traditional preparative gas chromatography (prep-GC). Here we show that radiocarbon values (Δ14C) of long-chain FAs, which originate from terrestrial higher plant waxes, reflect carbon from a substantially pre-aged OC reservoir, whereas the Δ14C of short-chain FAs that originate from aquatic sources were generally less pre-aged.14C ages obtained from the long-chain FAs are in closer agreement with14C ages of the corresponding bulk TOC fraction, indicating a high control of pre-aged terrestrial OC input from the catchment on TOC-derived14C ages. Variations in the age offset between terrestrial and aquatic biomarkers are related to changes in bulk sediment log(Ti/K) that reflect variations in detrital input from the catchment. Our results indicate that the chronological offset between terrestrial and aquatic OC in this high-altitude catchment is mainly driven by temporal variations in the mobilization of pre-aged OC from the catchment. In conclusion, to obtain accurate and process-specific lake sediment chronologies, attention must be given to the temporal dynamics of the RAE. Variations in the apparent ages of aquatic and terrestrial contributions to the sediment and their mass balance can substantially alter the reservoir age effect.

Highlights

  • Lake sediments provide excellent high-resolution archives of regional environmental and climatic changes in the past

  • In order to assure the purity of the collected fatty acid methyl esters (FAMEs) and to determine the recovery of carbon prior to 14C measurements, aliquots of 5 μL of several samples were run on a gas chromatograph (GC) equipped with a flame ionization detector (GC-FID, Agilent 7890B, Agilent Technologies, Santa Clara, United States) (Figure 2)

  • Because 14C analysis is sensitive to contributions from extraneous carbon (Cex), it is mandatory to assess the amount of Cex that is added to the sample during compound isolation and subsequent processing (Santos et al, 2007; Shah and Pearson, 2007; Mollenhauer and Rethemeyer, 2009; Ziolkowski and Druffel, 2009; Hanke et al, 2017)

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Summary

INTRODUCTION

Lake sediments provide excellent high-resolution archives of regional environmental and climatic changes in the past. To determine temporal variations in the RAE, compound-specific radiocarbon analysis (CSRA) of individual terrestrial and aquatic biomarkers is increasingly employed, as this method overcomes the mixed 14C signal of TOC dating (Smittenberg et al, 2004; Gierga et al, 2016). This can help to assess biomarker-specific transport characteristics and their residence times, thereby allowing an improved interpretation of processes that affect carbon cycling in various environmental settings (Eglinton et al, 1997; Makou et al, 2018). Due to the absence of fish stock, large numbers of the amphipod species Gammarus alius sp. nov., which is constrained to fresh and brackish water habitats, colonize aquatic plants (Sidorov, 2012)

MATERIALS AND METHODS
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CONCLUSION
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