The use of plant-specific pyrolysis products as biomarkers in peat deposits
Introduction
Peatlands respond to changes in environmental conditions. Proxies for such changes are preserved in the peat and may provide records of past environmental change (Chambers et al., 2012). Several studies of plant macrofossils in ombrotrophic peat have shown good correlations between vegetation composition and local hydrology (Blackford, 2000, Castro et al., 2015). Because in highly decomposed peat the preservation of plant remains is usually poor, plant-specific recalcitrant compounds (biomarkers) have been used instead of macrofossils to reconstruct plant species composition. Identified peatland biomarkers are relatively scarce (Nichols, 2010) and are mainly restricted to free solvent-extractable lipids (Dehmer, 1995, Pancost et al., 2002).
A biomarker approach assumes that biomarker abundance accurately reflects the original surface vegetation at the time of peat deposition (Blackford, 2000). Peat decomposition and changes in vegetation type have been found to influence biomarkers that are not plant-specific, such as the distribution of n-alkanes and the composition of lignin phenols. Decomposition may interfere with the plant-specific distribution of such compounds and cause errors in the hydrological interpretation (Pancost et al., 2002, Huang et al., 2012, Andersson and Meyers, 2012, Jex et al., 2014). The influence of decomposition, vegetation type and intrinsic plant characteristics appears more straightforward for plant specific markers, because these – contrary to n-alkanes and lignin phenols – have a single source. Nevertheless, effects of decomposition on specific markers have rarely been studied (Sinninghe-Damste et al., 2002). Therefore, the question arises to which extent the variation of a marker depends on the contribution from that particular plant species to the peat. It has recently been shown that the abundance of the marker for sphagnum acid, 4-isopropenylphenol, in Sphagnum-dominated peatlands reflects decomposition rather than the contribution from Sphagnum to the surface vegetation (Schellekens et al., 2015a). This demonstrates the need to study botanical changes and the degree of decomposition simultaneously.
Pyrolysis gas chromatography mass spectrometry (pyrolysis-GC/MS) gives a detailed fingerprint of organic material at the molecular level and enables studying the composition of biomacromolecules. The use of analytical pyrolysis to gain insight into peat decomposition processes has been repeatedly demonstrated (Halma et al., 1984, van Smeerdijk and Boon, 1987, Durig et al., 1989; van der Heijden et al., 1997, Kuder et al., 1998, Huang et al., 1998, Gleixner and Kracht, 2001, González et al., 2003, Buurman et al., 2006). Well-established macromolecular markers to differentiate between mosses and vascular plants include lignin phenols from lignin (Tsutsuki et al., 1994, Williams et al., 1998, Bourdon et al., 2000) and 4-isopropenylphenol from sphagnum acid (van der Heijden et al., 1997, Schellekens et al., 2009, Schellekens et al., 2015a, McClymont et al., 2011, Abbott et al., 2013, Swain and Abbott, 2013).
In addition to lignin phenols and 4-isopropenylphenol, the application of analytical pyrolysis in peat biomarker research was explored for a Sphagnum-dominated (Schellekens et al., 2009) and a graminoid-dominated (Schellekens et al., 2011) peatland. The results suggested that in addition to pyrolysis products of lignin and sphagnum acid, a number of specific markers can be used. Although within each study the hydrological interpretation of depth records of these markers agreed well with that of data obtained from other methods, their application needs verification.
In the present study, pyrolysates from 48 plants from Sphagnum-dominated and graminoid-dominated peatlands were combined in order to establish new biomarkers. The presence and behaviour of potential markers was tested and the ecological interpretation of their source plants discussed for six peat deposits from different climatic regions. In order to simplify the quantification procedure, depth records of the marker for sphagnum acid obtained by the traditional quantification (relative abundance) and by addition of an internal standard (5-α-androstane; absolute abundance by normalisation for organic carbon content) were compared. Thus, the purpose of this study was to establish methodological improvements in peatland biomarker research by i) the introduction of an internal standard using analytical pyrolysis, ii) identification of new biomarkers from pyrolysates of peatland plants and iii) identify whether the interpretation of biomarker depth records is consistent in diverse peatlands.
Section snippets
Peatlands
The selection of peatlands was designed to optimise testing the applicability of the markers. On the one hand, highly diverse peatlands were selected including different vegetation types (Sphagnum and graminoid-dominated) from boreal, temperate and tropical biomes, to test the application of potential biomarkers under different conditions. On the other hand, the solidity of the interpretation of marker records requires support from other hydrological proxies; therefore, the selected peatlands
Quantification of biomarkers from pyrolysates
The use of an internal standard to analyse biomarkers using analytical pyrolysis has been tested for the well-known marker for Sphagnum, 4-isopropenylphenol. For this purpose, samples from the upper 3 m of the Sphagnum-dominated HRB peat deposit were used. Depth records of 4-isopropenylphenol obtained with internal standard (mg 100 g−1) and traditional quantification (% of the total quantified pyrolysis products) are given in Fig. 1. The correlation between both is significant (r2 = 0.72, P
Conclusions
Plant specific pyrolysis products (biomarkers) were detected in all six peatlands, making pyrolysis-GC/MS a powerful method to reconstruct past vegetation composition from peatlands. Markers for lichens, graminoids and Sphagnum were present in all peatlands. The absence of depth trends indicates that none of the markers were subject to long-term anaerobic decomposition.
The similarity between depth records of the Sphagnum marker (4-isopropenylphenol) using an internal standard and the
Acknowledgements
This work was supported by FAPESP project 2013/03953-9 and CNPq project 482815/2001-6. The data from HRB were supported by BBVA Foundation; BIOCON05/119-CARBOCLIM project. We thank Richard Bindler (Umea University, Sweden) and Harald Biester (Braunschweig University, Germany) for disposal of the data from RMM and KM, respectively, and Alexandre Christófaro Silva from the Federal University of Mucuri and Jequitinhonha Valleys for the collaboration and discussion during the field campaigns for
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