Stable carbon and oxygen isotopes in sub-fossil Sphagnum ...
Stable carbon and oxygen isotopes in sub-fossil Sphagnum ...
Stable carbon and oxygen isotopes in sub-fossil Sphagnum ...
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<strong>Stable</strong> <strong>carbon</strong> <strong>and</strong> <strong>oxygen</strong> <strong>isotopes</strong> <strong>in</strong> <strong>sub</strong>-<strong>fossil</strong> <strong>Sphagnum</strong>: Assessment of their<br />
applicability for palaeoclimatology<br />
Robert Moschen a, ⁎, Norbert Kühl b , Ingo Rehberger c , Andreas Lücke a<br />
a Institute of Chemistry <strong>and</strong> Dynamics of the Geosphere: Agrosphere (ICG-4), Forschungszentrum Jülich, D-52425 Juelich, Germany<br />
b Ste<strong>in</strong>mann Institute of Geology, M<strong>in</strong>eralogy <strong>and</strong> Paleontology, University of Bonn, Germany<br />
c Institute of L<strong>and</strong>scape Ecology, University of Münster, Germany<br />
article <strong>in</strong>fo<br />
Article history:<br />
Received 19 May 2008<br />
Received <strong>in</strong> revised form 14 October 2008<br />
Accepted 14 November 2008<br />
Editor: B. Bourdon<br />
Keywords:<br />
<strong>Sphagnum</strong> peat<br />
Cellulose<br />
<strong>Stable</strong> <strong>carbon</strong> <strong>isotopes</strong><br />
Oxygen <strong>isotopes</strong><br />
Palaeoclimatology<br />
1. Introduction<br />
abstract<br />
The stable <strong>carbon</strong> <strong>and</strong> <strong>oxygen</strong> isotopic composition of plant<br />
organic matter has frequently been used for palaeoclimatic <strong>and</strong><br />
palaeoenvironmental reconstructions. Wood is the preferred material<br />
for such studies which found empirical relationships between plant<br />
isotopic ratios <strong>and</strong> different climatic parameters, <strong>in</strong>clud<strong>in</strong>g temperature<br />
<strong>and</strong> relative humidity (e.g. DeNiro <strong>and</strong> Epste<strong>in</strong>, 1981; Edwards<br />
et al., 1985; Sternberg et al., 1986). Bulk plant tissue is composed of a<br />
number of chemical components that differ <strong>in</strong> their proportions<br />
between species. In dendroclimatological research, plant cellulose is<br />
⁎ Correspond<strong>in</strong>g author. Tel.: +49 2461 61 5464; fax: +49 2461 61 2484.<br />
E-mail address: r.moschen@fz-juelich.de (R. Moschen).<br />
0009-2541/$ – see front matter © 2008 Elsevier B.V. All rights reserved.<br />
doi:10.1016/j.chemgeo.2008.11.009<br />
Chemical Geology 259 (2009) 262–272<br />
Contents lists available at ScienceDirect<br />
Chemical Geology<br />
journal homepage: www.elsevier.com/locate/chemgeo<br />
To <strong>in</strong>vestigate the potential of stable <strong>isotopes</strong> of <strong>Sphagnum</strong> peat deposits for palaeoclimate research <strong>and</strong> to<br />
<strong>in</strong>form sampl<strong>in</strong>g strategies, we present results from a study of selected <strong>Sphagnum</strong> plant constituents. We<br />
report a comb<strong>in</strong>ed stable <strong>carbon</strong> <strong>and</strong> <strong>oxygen</strong> isotope record of cellulose separately extracted from <strong>Sphagnum</strong><br />
branches <strong>and</strong> stem sections manually sampled from a ∼4000 year old peat, deposited <strong>in</strong> a small dry maar<br />
crater located <strong>in</strong> the Westeifel Volcanic Field, Germany. We have determ<strong>in</strong>ed the species composition of each<br />
<strong>in</strong>dividual sample of <strong>Sphagnum</strong> branches to address the sensitivity of the stable isotope records to potential<br />
changes <strong>in</strong> <strong>Sphagnum</strong> assemblages. The youngest approximately 3000 years old peat section consists of<br />
scarcely decomposed <strong>Sphagnum</strong> plant material. From the bog's surface to a depth of ∼60 cm the<br />
predom<strong>in</strong>ant species is <strong>Sphagnum</strong> magellanicum. Between ∼60 <strong>and</strong> ∼550 cm the peat predom<strong>in</strong>antly<br />
consists of <strong>Sphagnum</strong> capillifolium var. rubellum. At greater depths the decomposition status <strong>in</strong>creases,<br />
species identification is, however, solely achievable if the record under exam<strong>in</strong>ation consists of moderately<br />
decomposed peat. The stable <strong>carbon</strong> <strong>and</strong> <strong>oxygen</strong> isotope values of cellulose from <strong>Sphagnum</strong> stem sections are<br />
significantly lighter than those of the branches. Both isotopic offsets between the different plant compounds<br />
exhibit a strong degree of correlation, are statistically highly significant <strong>and</strong> observable down-core. The stable<br />
<strong>carbon</strong> isotope offset averages to 1.5‰, however, presumably decreases with <strong>in</strong>creas<strong>in</strong>g age of the plant<br />
material. In contrast, the averaged <strong>oxygen</strong> isotope offset of 0.9‰ is consistent <strong>in</strong> time. Our results imply that<br />
if no differentiation <strong>in</strong>to <strong>Sphagnum</strong> branches <strong>and</strong> stem sections prior to stable isotope analyses is possible,<br />
erroneous <strong>in</strong>terpretations of the isotope records are likely, s<strong>in</strong>ce down-core changes <strong>in</strong> the ratio of branches<br />
to stem sections <strong>in</strong> the peat profile are most likely. This also implies that the removal of all non-<strong>Sphagnum</strong><br />
plants or plant fragments is <strong>in</strong>sufficient to retrieve stable isotope signals from peat deposits exclusively<br />
reflect<strong>in</strong>g palaeo-environmental conditions. Even isotopic records from bulk <strong>Sphagnum</strong> cellulose comprise of<br />
two different signals: firstly, an environmental signal based on the plant response to external controls. This<br />
signal is, however, masked by a second plant physiological signal orig<strong>in</strong>at<strong>in</strong>g from the isotopic offset between<br />
branches <strong>and</strong> stem sections.<br />
© 2008 Elsevier B.V. All rights reserved.<br />
usually used for stable isotope studies s<strong>in</strong>ce this s<strong>in</strong>gle chemical<br />
fraction allows l<strong>in</strong>k<strong>in</strong>g the isotopic signal to a specific growth period <strong>in</strong><br />
the annual cycle of wood formation (Helle <strong>and</strong> Schleser, 2004).<br />
Moreover, isolation of a s<strong>in</strong>gle chemical component reduces problems<br />
associated with changes <strong>in</strong> the relative proportion of chemical<br />
compounds over time (R<strong>in</strong>ne et al., 2005).<br />
Despite the great potential of peat bogs as climate archives, to<br />
date only few stable isotope studies focus on cellulose derived<br />
from cont<strong>in</strong>uously accumulated peat deposits. These archives<br />
provide records of environmental changes <strong>and</strong> vegetation<br />
dynamics over time, are widely distributed, <strong>and</strong> cover a large<br />
part of the earth's l<strong>and</strong> surface often with<strong>in</strong> human habitat<br />
(Charman, 2002). They can have relatively high accumulation<br />
rates <strong>and</strong> botanical <strong>fossil</strong>s such as pollen <strong>and</strong> plant macro<strong>fossil</strong>s are<br />
often well preserved due to the <strong>oxygen</strong> poor conditions <strong>in</strong> peat.
Peat deposits are, therefore, an ideal archive for comb<strong>in</strong><strong>in</strong>g<br />
isotope-geochemical studies with palynological <strong>and</strong> palaeoecological<br />
approaches (Brenn<strong>in</strong>kmeijer et al., 1982). <strong>Sphagnum</strong> is the<br />
most abundant peat form<strong>in</strong>g genus <strong>in</strong> ombrotrophic bogs <strong>and</strong> fens<br />
<strong>in</strong> northern <strong>and</strong> western Europe <strong>and</strong> abundant <strong>in</strong> peat records<br />
throughout large time spans of the Holocene (Clymo, 1970). Recent<br />
studies have systematically <strong>in</strong>vestigated the relationship between<br />
climate parameters <strong>and</strong> cellulose isotope ratios <strong>in</strong> modern <strong>Sphagnum</strong><br />
plants (e.g. Proctor et al., 1992; Aucour et al., 1996; Ménot <strong>and</strong><br />
Burns, 2001; Ménot-Combes et al., 2002; Zanazzi <strong>and</strong> Mora, 2005;<br />
Skrzypek et al., 2007). Also a number of studies have attempted to<br />
use the isotopic compositions of <strong>sub</strong>-<strong>fossil</strong> peat material to <strong>in</strong>fer<br />
environmental <strong>and</strong>/or climatic changes over time (Brenn<strong>in</strong>kmeijer<br />
et al., 1982; Aucour et al., 1996; Turney et al., 1997; Hong et al.,<br />
2000, 2001; Jędrysek <strong>and</strong> Skrzypek, 2005). These studies, however,<br />
focus on bulk peat material <strong>and</strong> provided somewhat ambiguous<br />
results. Peat deposits are usually a mixture of partly decayed plant<br />
materials from different species. Use of bulk peat material,<br />
therefore, can be problematic due to contributions from multiple<br />
plants <strong>and</strong> fungi <strong>and</strong>/or selective degradation of isotopically<br />
dist<strong>in</strong>ct compounds (Pancost et al., 2003). A further problem<br />
must be seen <strong>in</strong> the fact that peat bogs are composed of a variety of<br />
different microenvironments that exhibit considerable variations<br />
<strong>in</strong> terms of bog wetness <strong>and</strong> moisture level. Bog vegetation, thus,<br />
typically consists of different <strong>Sphagnum</strong> species <strong>and</strong> sedges. S<strong>in</strong>ce<br />
different peatl<strong>and</strong> species have been shown to be related to<br />
environmental- or climatic parameters <strong>in</strong> a different degree,<br />
analys<strong>in</strong>g bulk peat material ignores the possible complicat<strong>in</strong>g<br />
factor of changes <strong>in</strong> <strong>Sphagnum</strong> species or species composition <strong>in</strong> a<br />
peat deposit (Ménot-Combes et al., 2002). Despite the great<br />
potential for environmental reconstructions, the application of<br />
<strong>sub</strong>-<strong>fossil</strong> <strong>Sphagnum</strong> cellulose of bulk organic matter from peat<br />
deposits as a valid palaeoclimate proxy, therefore, is still uncerta<strong>in</strong>.<br />
An advanced contribution to test the potential of stable <strong>carbon</strong><br />
<strong>isotopes</strong> of <strong>Sphagnum</strong> as palaeoclimate proxy was accomplished by<br />
Loader et al. (2007). The authors <strong>in</strong>vestigated <strong>in</strong>ter- <strong>and</strong> <strong>in</strong>tra-plant<br />
stable <strong>carbon</strong> isotopic variability of different physical components<br />
of <strong>in</strong>dividual modern <strong>Sphagnum</strong> plants. The results revealed a<br />
significant isotopic offset between branches <strong>and</strong> stems.<br />
To explore the potential of stable <strong>isotopes</strong> of selected <strong>Sphagnum</strong><br />
peat constituent for palaeoclimate research, we present results<br />
from a study of cellulose stable <strong>isotopes</strong> from selected <strong>Sphagnum</strong><br />
constituents. We report the first comb<strong>in</strong>ed δ 13 C<strong>and</strong>δ 18 Orecordof<br />
<strong>Sphagnum</strong> cellulose separately extracted from <strong>Sphagnum</strong> branches<br />
<strong>and</strong> stem sections manually separated from an approximately<br />
4000 year old peat deposit. The ma<strong>in</strong> goals of this study are as<br />
follows. First, we sought to better underst<strong>and</strong> the isotopic<br />
variability of different physical <strong>Sphagnum</strong> plant components <strong>in</strong><br />
<strong>sub</strong>-<strong>fossil</strong> peat material. The manual separation of branches <strong>and</strong><br />
stem sections prior to stable isotope analyses should allow<br />
determ<strong>in</strong><strong>in</strong>g possible stable isotope offsets between these different<br />
plant components. Second, we attempt to <strong>in</strong>vestigate the species<br />
composition of each <strong>in</strong>dividual sample down core to address the<br />
sensitivity of the stable isotope records to potential changes <strong>in</strong><br />
<strong>Sphagnum</strong> assemblages. S<strong>in</strong>ce different <strong>Sphagnum</strong> species are<br />
assumed to be related to changes <strong>in</strong> bog ecology <strong>in</strong> a different<br />
degree, this approach also address the sensitivity of the records to<br />
potential changes <strong>in</strong> bog ecosystem variations. The aim of this study<br />
is, moreover, to <strong>in</strong>form sampl<strong>in</strong>g strategies for application of stable<br />
<strong>isotopes</strong> from <strong>Sphagnum</strong> plant material to the palaeorecord. An<br />
improved underst<strong>and</strong><strong>in</strong>g of the isotope variability <strong>in</strong> <strong>sub</strong>-<strong>fossil</strong><br />
<strong>Sphagnum</strong> plant components will significantly contribute to the<br />
evaluation of the potential of stable isotope signals from peat<br />
deposits <strong>and</strong> address to the reliability of such archives to record<br />
climatic <strong>and</strong>/or environmental <strong>in</strong>formation on the basis of stable<br />
isotope analysis.<br />
R. Moschen et al. / Chemical Geology 259 (2009) 262–272<br />
2. Background<br />
2.1. <strong>Stable</strong> <strong>carbon</strong> isotope ratios of <strong>Sphagnum</strong> cellulose<br />
<strong>Sphagnum</strong> does not have stomata <strong>and</strong> is therefore unable to<br />
regulate its uptake of CO 2 through any physiological response.<br />
Photosynthetic cells are surrounded by large, dead so called “hyal<strong>in</strong>e<br />
cells”, which form significant water reservoirs. Carbon dioxide enters<br />
the plant through pores <strong>in</strong> the hyal<strong>in</strong>e cells <strong>and</strong> diffuses through the<br />
water that surrounds the chloroplast. The water filled hyal<strong>in</strong>e cells<br />
build large barriers for <strong>carbon</strong> assimilation, because the diffusivity of<br />
CO2 is much lower <strong>in</strong> water than <strong>in</strong> air. S<strong>in</strong>ce the <strong>carbon</strong> isotope<br />
discrim<strong>in</strong>ation dur<strong>in</strong>g photosynthesis is <strong>in</strong> general similar for mosses<br />
to that for vascular plants, the forward resistance of <strong>Sphagnum</strong> mosses<br />
to CO 2 is more complicated (White et al., 1994; Ménot <strong>and</strong> Burns,<br />
2001).<br />
<strong>Sphagnum</strong> can absorb or lose water more rapidly than vascular<br />
plants <strong>and</strong> stable <strong>carbon</strong> isotope fractionation <strong>and</strong> the stable<br />
<strong>carbon</strong> isotope composition of the cellulose extracted from<br />
<strong>Sphagnum</strong> plant material (δ 13 Ccellulose) depend greatly on water<br />
availability which can vary between two extreme conditions:<br />
when the peat surface is relatively dry <strong>and</strong> hyal<strong>in</strong>e cells are little<br />
filled with water, CO 2 diffusion to the chloroplast is relatively high.<br />
Carbon fixation is limited by reduced metabolic activity <strong>and</strong> the<br />
δ 13 C cellulose values are dom<strong>in</strong>ated by <strong>carbon</strong> isotope fractionation<br />
due to the photosynthetic enzyme. This desiccation effect results<br />
<strong>in</strong> an <strong>in</strong>crease <strong>in</strong> discrim<strong>in</strong>ation aga<strong>in</strong>st 13 CO 2 dur<strong>in</strong>g photosynthesis<br />
(Williams <strong>and</strong> Flanagan, 1996). In contrast, if a peat bog is<br />
relatively wet <strong>and</strong> water availability for <strong>Sphagnum</strong> plants is good,<br />
the hyal<strong>in</strong>e cells are highly filled with water. Diffusion of CO2 to<br />
the chloroplasts is reduced <strong>and</strong> δ 13 C cellulose values are predom<strong>in</strong>antly<br />
<strong>in</strong>fluenced by stable <strong>carbon</strong> isotope fractionation (Ménot<br />
<strong>and</strong> Burns, 2001). Consequently, the smaller the water reservoir<br />
surround<strong>in</strong>g the chloroplast is, the lower is the δ 13 Ccellulose of<br />
<strong>Sphagnum</strong> mosses, <strong>and</strong> vice versa. Thus, there is a great potential<br />
for the stable <strong>carbon</strong> isotope ratio <strong>in</strong> <strong>Sphagnum</strong> to record changes<br />
<strong>in</strong> bog wetness, which can be presumably related to climate<br />
variability.<br />
2.2. Oxygen isotope ratios of <strong>Sphagnum</strong> cellulose<br />
In general, the <strong>oxygen</strong> isotopic composition of plant cellulose<br />
depends on the isotopic composition of the source water, the<br />
enrichment of heavier <strong>isotopes</strong> <strong>in</strong> leaf water due to evapotranspiration<br />
<strong>and</strong> the overall biochemical fractionation between source water <strong>and</strong><br />
cellulose (Brenn<strong>in</strong>kmeijer et al., 1982). Due to the absence of stomata<br />
<strong>and</strong> vascular tissues, <strong>Sphagnum</strong> mosses possess a simpler water use<br />
strategy. Their limited ability to control water loss forces them to a<br />
relative simple physiological strategy: they <strong>in</strong>habit environments with<br />
high relative humidity or niches characterized by complete wetness.<br />
At low water content, assimilation <strong>and</strong> cellulose biosynthesis is<br />
reduced due to an overall decrease <strong>in</strong> metabolic processes. Photosynthetic<br />
rates, however, are also <strong>in</strong>hibited due to diffusional<br />
limitation imposed by excess water (Williams <strong>and</strong> Flanagan, 1996).<br />
Experimental <strong>and</strong> observational measurements on different <strong>Sphagnum</strong><br />
species <strong>in</strong>dicate that the overall enrichment factor between the<br />
source water <strong>and</strong> <strong>Sphagnum</strong> cellulose dur<strong>in</strong>g cellulose biosynthesis is<br />
27 ± 3‰ for <strong>oxygen</strong> <strong>isotopes</strong> (Zanazzi <strong>and</strong> Mora, 2005). This enrichment<br />
factor has former been described for terrestrial <strong>and</strong> aquatic<br />
plants <strong>and</strong> is likely to be <strong>in</strong>sensitive to temperature (DeNiro <strong>and</strong><br />
Epste<strong>in</strong>, 1979; DeNiro <strong>and</strong> Epste<strong>in</strong>, 1981; Sternberg et al., 1986).<br />
Consequently, the <strong>oxygen</strong> isotope composition of the cellulose<br />
extracted from <strong>Sphagnum</strong> plant material (δ 18 Ocellulose) should be a<br />
potential recorder for changes <strong>in</strong> the <strong>oxygen</strong> isotopic composition of<br />
the plants source water <strong>and</strong> should provide <strong>in</strong>formation of isotopically<br />
changes <strong>in</strong> bog hydrology.<br />
263
264 R. Moschen et al. / Chemical Geology 259 (2009) 262–272<br />
2.3. Implications to the potential of stable <strong>isotopes</strong> of <strong>Sphagnum</strong> cellulose<br />
for palaeoenvironmental research<br />
It has been considered that the δ 13 Ccellulose of <strong>Sphagnum</strong> mosses<br />
records changes <strong>in</strong> bog wetness (DeNiro <strong>and</strong> Epste<strong>in</strong>, 1981) <strong>and</strong><br />
assumed that the δ 18 Ocellulose of <strong>Sphagnum</strong> mosses should be a<br />
potential recorder for changes <strong>in</strong> the <strong>oxygen</strong> isotopic composition of<br />
the plants source water (Hong et al., 2001; Ménot-Combes et al.,<br />
2002). Thus, a comb<strong>in</strong>ation of stable <strong>carbon</strong> <strong>and</strong> <strong>oxygen</strong> isotope<br />
measurements might be an adequate approach to provide <strong>in</strong>formation<br />
of changes <strong>in</strong> bog hydrology, relatable to source water <strong>and</strong> climate<br />
variability. Such approach may offer the possibility to <strong>in</strong>fer past<br />
hydrological conditions of peat deposits which form high-resolution<br />
cont<strong>in</strong>ental records up to the entire Holocene.<br />
3. Material <strong>and</strong> methods<br />
3.1. Study site<br />
In 2006 we took a core from a peat deposit located <strong>in</strong> the “Dürres<br />
Maar” (50°52'N, 6°53'E; 455 m a.s.l.), a small dry maar crater situated <strong>in</strong><br />
the mounta<strong>in</strong>ous Westeifel Volcanic Field, Germany. The geological<br />
basement consists almost exclusively of Devonian shales. On this<br />
bedrock relatively poor non-calcarous soils developed <strong>in</strong> the surround<strong>in</strong>g<br />
of the maar crater without surficial <strong>in</strong>flow <strong>and</strong> outflow (Forst et al.,<br />
1997). The current mesotrophic bog has a diameter of 140–175 m with a<br />
surface area of 0.029 km 2 <strong>and</strong> is 455 m a.s.l. The maximum elevation of<br />
the crater rim is 470 m a.s.l. (Fig. 1). In the centre of the current bog the<br />
peat deposit has a thickness of approximately 12 m. The surface of the<br />
bog is wet, but walkable, <strong>and</strong> two vegetation zones can be dist<strong>in</strong>guished,<br />
which are ma<strong>in</strong>ly due to hydrological conditions <strong>and</strong> nutrient supply.<br />
Closest to the edge <strong>and</strong> wettest is the lagg, where Carex lasiocarpa <strong>and</strong> C.<br />
rostrata dom<strong>in</strong>ate <strong>and</strong> where fen taxa exist such as Potentilla palustris.A<br />
transitional zone follows towards the central bog area where the<br />
vegetation consists of raised bog species. Dom<strong>in</strong>at<strong>in</strong>g elements are<br />
<strong>Sphagnum</strong> magellanicum, S. capillifolium var. rubellum <strong>in</strong> comb<strong>in</strong>ation<br />
with S. fallax, S. angustifolium, Vacc<strong>in</strong>ium oxycoccos, Eriophorum<br />
angustifolium <strong>and</strong> E. vag<strong>in</strong>atum. Several small birchs (Betula pubescens)<br />
<strong>and</strong> scattered small p<strong>in</strong>es (P<strong>in</strong>us sylvestris) cover the current bog (Fig. 2,<br />
Forst et al., 1997).<br />
Fig. 1. Location of Dürres Maar <strong>and</strong> map of Dürres Maar <strong>and</strong> the nearby Lake Holzmaar.<br />
3.2. Core collection<br />
We have recovered the core <strong>in</strong> the centre of the peat deposit us<strong>in</strong>g<br />
two different cor<strong>in</strong>g devices: the uppermost 3 m of the deposit were<br />
cored with a lopsided open peat corer provid<strong>in</strong>g sections of 1 m length<br />
<strong>and</strong> 6.0 cm diameter. The <strong>Sphagnum</strong> peat conta<strong>in</strong>s some small 'water<br />
lenses' requir<strong>in</strong>g a different cor<strong>in</strong>g device for greater depths <strong>in</strong> order<br />
to avoid core loss from the lopsided open cor<strong>in</strong>g device. The use of a<br />
Russian corer at depths greater than 3 m avoided core loss due to the<br />
closure of the cor<strong>in</strong>g device. The Russian corer allows to core sections<br />
of 50 cm length with a diameter of 5.5 cm.<br />
The s<strong>in</strong>gle core sections were carefully packed <strong>in</strong> plastic half-shells<br />
(semi-tubes) of the same length <strong>and</strong> diameter as the recovered<br />
sections. Each section was wrapped with t<strong>in</strong>foil, labelled, packed <strong>in</strong>to<br />
robust polyurethane bags, <strong>and</strong> packed horizontally <strong>in</strong> rows <strong>in</strong><br />
transport boxes. After remov<strong>in</strong>g a section the corer was cleaned<br />
with deionised water. Ore sections were stored at the Institute of Crop<br />
Fig. 2. Aerial photograph of Dürres Maar with borehole location.
Science <strong>and</strong> Resource Conservation (Institut für Nutzpflanzenwissenschaften<br />
und Ressourcenschutz, INRES) <strong>in</strong> Bonn, Germany <strong>in</strong> a<br />
walkable freezer at −24 °C. The <strong>in</strong>vestigated core material consists of a<br />
relatively pure <strong>and</strong> slightly decomposed <strong>Sphagnum</strong> peat, temporary<br />
<strong>in</strong>termitted by small water lenses.<br />
3.3. Sampl<strong>in</strong>g<br />
Each frozen core section was cut <strong>in</strong>to 2 cm <strong>in</strong>crements <strong>in</strong> the lab<br />
under room temperature us<strong>in</strong>g a sta<strong>in</strong>less steel h<strong>and</strong> saw <strong>in</strong><br />
comb<strong>in</strong>ation with a mitre lay. The width of the blade is 1 mm,<br />
which causes an approximately 5% loss of each slice dur<strong>in</strong>g cutt<strong>in</strong>g.<br />
Immediately after cutt<strong>in</strong>g, the outermost ∼2 mm of each deep frozen<br />
slice was removed <strong>and</strong> the samples were additionally washed<br />
carefully with deionised water to remove possible contam<strong>in</strong>ations<br />
with plant fragments orig<strong>in</strong>at<strong>in</strong>g from lower depths of the record or<br />
adheres to the core dur<strong>in</strong>g field work (Givelet et al., 2004).<br />
3.4. 14 C dat<strong>in</strong>g<br />
The used core section was dated us<strong>in</strong>g multiple AMS radio<strong>carbon</strong><br />
dates <strong>and</strong> was found to cover the last approximately 4000 years. 13<br />
samples consist<strong>in</strong>g of pure <strong>Sphagnum</strong> plant fragments, each cover<strong>in</strong>g a<br />
2 cm depth <strong>in</strong>terval of the core were <strong>sub</strong>mitted for radio<strong>carbon</strong> dat<strong>in</strong>g<br />
to the Poznań Radio<strong>carbon</strong> Laboratory at Poznań, Pol<strong>and</strong>. Pure<br />
<strong>Sphagnum</strong> is used for radio<strong>carbon</strong> dat<strong>in</strong>g because it forms the<br />
predom<strong>in</strong>ant part of the “Dürres Maar” peat deposit, does not have<br />
roots <strong>and</strong> grows <strong>in</strong> an upward direction from the apex. There is little<br />
possibility for this plant to derive <strong>carbon</strong> from the underly<strong>in</strong>g older<br />
peat. In one case (Sample Poz-23192 from a depth of 5.76–580 m)<br />
plant fragments from Vacc<strong>in</strong>ium spec. were used for 14 C dat<strong>in</strong>g,<br />
because <strong>Sphagnum</strong> was not available <strong>in</strong> an adequate amount. Samples<br />
were treated chemically accord<strong>in</strong>g to the st<strong>and</strong>ard acid–alkali–acid<br />
procedure. The details of the laboratory procedure are described by<br />
Czernik <strong>and</strong> Goslar (2001).<br />
3.5. Separation of <strong>Sphagnum</strong> branches <strong>and</strong> stem sections from the<br />
core material<br />
Before different components of <strong>Sphagnum</strong> plants could be<br />
manually separated from <strong>in</strong>dividual bulk peat samples, approximately<br />
5 to 6 g wet peat were placed <strong>in</strong> 800 ml beakers <strong>in</strong> deionised water on<br />
a heatable magnetic stirrer <strong>and</strong> were simmered for one hour at 85 °C.<br />
Subsequently, each sample was carefully wet sieved on a 630 µm sieve<br />
with approximately 5 l of deionised water to separate the f<strong>in</strong>e fraction<br />
from the <strong>Sphagnum</strong> moss plants <strong>and</strong> other plant fragments rema<strong>in</strong><strong>in</strong>g<br />
on the 630 µm sieve.<br />
Due to simmer<strong>in</strong>g <strong>and</strong> siev<strong>in</strong>g the peat samples were easily<br />
fragmented <strong>in</strong>to s<strong>in</strong>gle branches or even branch fragments <strong>and</strong> the<br />
less fragile stem sections. The N630 µm sieve fraction predom<strong>in</strong>antly<br />
consists of <strong>Sphagnum</strong> plant fragments of different dimension. This<br />
fraction also conta<strong>in</strong>s variable amounts of plant fragments from<br />
Cyperaceae (ma<strong>in</strong>ly Eriophorum spec.) <strong>and</strong> Vacc<strong>in</strong>ium (<strong>sub</strong>genus Oxycoccus).<br />
Manually pick<strong>in</strong>g of s<strong>in</strong>gle <strong>Sphagnum</strong> branches <strong>and</strong> stem<br />
sections from the N630 µm sieve fraction of the core material was<br />
carried out under a stereozoom microscope (Nikon SMZ 2B).<br />
Individual <strong>Sphagnum</strong> branch samples used for cellulose extraction<br />
consist of approximately 350 to 400 branches. Due to the higher<br />
weight of the stem sections, samples of stem sections consist of<br />
approximately 130 to 150 <strong>in</strong>dividual stem sections.<br />
3.6. <strong>Sphagnum</strong> species identification<br />
The genus <strong>Sphagnum</strong> comprises of two <strong>sub</strong>-genera with over 40<br />
species <strong>in</strong> Europe (Smith, 2004). It is not always possible to identify<br />
<strong>Sphagnum</strong> spp. from peat deposits to species level, particularly<br />
R. Moschen et al. / Chemical Geology 259 (2009) 262–272<br />
when their stem-leaves are absent, which are very important for<br />
identification (Mauquoy <strong>and</strong> van Geel, 2007). However, <strong>Sphagnum</strong><br />
branches are often preserved <strong>and</strong> most of the common European<br />
ombrotrophic species are readily determ<strong>in</strong>able by the morphological<br />
characteristics of the hyal<strong>in</strong>e cells <strong>and</strong> the position of the chlorophyllose<br />
cells of the small s<strong>in</strong>gle leaves cover<strong>in</strong>g <strong>Sphagnum</strong> branches.<br />
Species determ<strong>in</strong>ation was accomplished us<strong>in</strong>g a Nikon stereozoom<br />
microscope (SMZ 2B) follow<strong>in</strong>g the <strong>in</strong>structions given by Barber<br />
(1981) <strong>and</strong> Mauquoy <strong>and</strong> van Geel (2007).<br />
In north-western Europe four cymbifolian leave species (boatshaped,<br />
cucullate, <strong>and</strong> relatively big leaves) of the <strong>sub</strong>-genus Inophloea<br />
(<strong>Sphagnum</strong> imbricatum, S. papillosum, S. magellanicum, <strong>and</strong><br />
S. palustre) have to be dist<strong>in</strong>guished from <strong>Sphagnum</strong> cuspidatum <strong>and</strong><br />
<strong>Sphagnum</strong> section Acutifolia (<strong>in</strong>clud<strong>in</strong>g S. fuscum, S. capillifolium var.<br />
rubellum <strong>and</strong> S. <strong>sub</strong>nitens) from the <strong>sub</strong>-genus Litophloea with<br />
relatively small leaves. Leaves from <strong>Sphagnum</strong> section Acutifolia are<br />
readily recognized by their ovate to narrow-ovate branch leaves,<br />
which are small <strong>in</strong> S. fuscum <strong>and</strong> S. capillifolium (0.8–1.3 mm) <strong>and</strong><br />
rather bigger <strong>in</strong> S. <strong>sub</strong>nitens an S. molle (1.2–2.7 mm). A consistent<br />
identification to the species level is, however, difficult unless stemleaves<br />
are present, s<strong>in</strong>ce the morphology of the hyal<strong>in</strong>e cells does not<br />
differ <strong>in</strong> <strong>Sphagnum</strong> section Acutifolia (Barber, 1981; Smith, 2004).<br />
Individual <strong>Sphagnum</strong> branch samples used for cellulose extraction<br />
consist of approximately 350 to 400 branches to obta<strong>in</strong><strong>in</strong>g enough<br />
cellulose for isotopic measurements. S<strong>in</strong>ce systematic scann<strong>in</strong>g of<br />
every s<strong>in</strong>gle branch for morphological characterisations of its hyal<strong>in</strong>e<br />
cells is unrealistic, we decided to separate 12 s<strong>in</strong>gle branches from<br />
each sample for species determ<strong>in</strong>ation. A summary weightedaverag<strong>in</strong>g<br />
ord<strong>in</strong>ation technique was employed to estimate the<br />
statistical species composition of each entire branch sample (Dupont,<br />
1986).<br />
3.7. Cellulose extraction <strong>and</strong> stable isotope measurements<br />
We have extracted cellulose separately from the <strong>Sphagnum</strong><br />
branches <strong>and</strong> stem sections us<strong>in</strong>g an improved extraction method<br />
based on sample bleach<strong>in</strong>g with sodium chlorite <strong>and</strong> a follow<strong>in</strong>g<br />
cellulose dissolution <strong>and</strong> re-precipitation with cuprammonium solution<br />
(CUAM). After conventional sodium chlorite bleach<strong>in</strong>g follow<strong>in</strong>g<br />
the method described by Ménot <strong>and</strong> Burns (2001), cellulose was<br />
dissolved <strong>in</strong> the CUAM solution ([Cu(NH3)4](OH)2) <strong>and</strong> re-precipitated<br />
us<strong>in</strong>g sulphuric acid (Wissel et al., 2008). CUAM is an aqueous metal<br />
complex solution well known for its capability of dissolv<strong>in</strong>g cellulose<br />
<strong>in</strong> pulp chemistry (Saalwächter et al., 2000). Contrary to the Ménot<br />
<strong>and</strong> Burns method, no solvent extraction stage prior to the extraction<br />
of cellulose was carried out, s<strong>in</strong>ce this step has been found to be<br />
unessential for the purification of cellulose even from res<strong>in</strong>ous woods<br />
(R<strong>in</strong>ne et al., 2005). Compared to conventional methods the CUAM<br />
approach achieves prist<strong>in</strong>e cellulose not by remov<strong>in</strong>g any contam<strong>in</strong>ants<br />
from the cellulose, but by dissolv<strong>in</strong>g the desire, i.e. the cellulose<br />
from bulk organic matter. That way, contam<strong>in</strong>ations of <strong>Sphagnum</strong><br />
cellulose with small amounts of m<strong>in</strong>erogenic matter like silt <strong>and</strong> clay<br />
<strong>and</strong>/or biogenic opal could be completely excluded. Received cellulose<br />
is highly homogenous ensur<strong>in</strong>g isotopic homogeneity when us<strong>in</strong>g<br />
small sample amounts for isotope measurements.<br />
<strong>Stable</strong> <strong>carbon</strong> isotope ratios of <strong>Sphagnum</strong> cellulose were measured<br />
by on-l<strong>in</strong>e combustion of 200–300 µg dry cellulose weighted <strong>in</strong>to t<strong>in</strong><br />
foil cups <strong>and</strong> combusted at 1080 °C us<strong>in</strong>g an EuroEA elemental<br />
analyser (Euro Vector Instruments, Italy) to generate CO2 for an<br />
<strong>in</strong>terfaced IsoPrime cont<strong>in</strong>uous flow isotope ratio mass spectrometer<br />
(GV Instruments, United K<strong>in</strong>gdom).<br />
Oxygen isotope ratios of <strong>Sphagnum</strong> cellulose were measured by<br />
on-l<strong>in</strong>e combustion of approximately 275 µg dry cellulose weighted<br />
<strong>in</strong>to silver foil cups which were afterwards vacuum-dried <strong>and</strong><br />
<strong>sub</strong>sequently pyrolysed at 1450 °C us<strong>in</strong>g an high temperature<br />
pyrolysis analyser (HT-O, HEKAtech, Germany) to generate CO for<br />
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266 R. Moschen et al. / Chemical Geology 259 (2009) 262–272<br />
Table 1<br />
Results of radio<strong>carbon</strong> dat<strong>in</strong>g: <strong>Sphagnum</strong> plant material is used for radio<strong>carbon</strong> dat<strong>in</strong>g<br />
because it forms the predom<strong>in</strong>ant part of the “Dürres Maar” peat deposit<br />
Depth [cm] Lab. no.<br />
14<br />
C age Cal. BP Calendar age<br />
68–70 Poz-22242 285±30 BP 457–347 1548±55 AD<br />
132–134 Poz-23191 890±30 BP 834–733 1167 ± 51 AD<br />
172–174 Poz-22243 1075± 30 BP 1015–930 978 ±43 AD<br />
228–230 Poz-20797 1140±30 BP 1142–968 895 ±87 AD<br />
308–310 Poz-22244 1270± 30 BP 1286–1167 724±60 AD<br />
380–382 Poz-20798 1490±30 BP 1416–1305 590 ±56 AD<br />
428–430 Poz-22246 1570± 30 BP 1530–1393 489±69 AD<br />
460–462 Poz-20799 1585±30 BP 1538–1405 479 ±67 AD<br />
516–518 Poz-20773 1650±30 BP 1622–1508 385 ±57 AD<br />
576–580 Poz-23192⁎ 2125±35 BP 2160–1997 129 ±82 BC<br />
626–628 Poz-20800 2585±30 BP 2766–2701 784 ±33 BC<br />
668–670 Poz-22247 3030±35 BP 3355–3143 1299 ±106 BC<br />
716–718 Poz-20801 3495±35 BP 3865–3689 1827±88 BC<br />
In one case (⁎) from a depth of 576–580 cm plant fragments from Vacc<strong>in</strong>ium spec. were<br />
used for 14 C dat<strong>in</strong>g, because <strong>Sphagnum</strong> plant material was not available <strong>in</strong> an adequate<br />
amount. St<strong>and</strong>ard deviation for the calendar ages is given as 1σ.<br />
the same <strong>in</strong>terfaced IsoPrime cont<strong>in</strong>uous flow isotope ratio mass<br />
spectrometer (GV Instruments, United K<strong>in</strong>gdom). Each sample was<br />
measured at least 3 times.<br />
Results are reported us<strong>in</strong>g the conventional δ-notation (δ =(R S /<br />
RSt − 1)⁎1000) with RS <strong>and</strong> RSt as isotope ratios ( 13 C/ 12 C, 18 O/ 16 O) of<br />
samples <strong>and</strong> st<strong>and</strong>ards (V-PDB for <strong>carbon</strong>, V-SMOW for <strong>oxygen</strong>),<br />
respectively. USGS24 graphite <strong>and</strong> Merk cellulose were used as<br />
reference materials (Boettger et al., 2007). Two <strong>in</strong>ternal st<strong>and</strong>ards<br />
(Fluka cellulose <strong>and</strong> graphite) were used for drift corrections. The overall<br />
precision of replicate analyses is estimated to be better than ±0.1‰ for<br />
δ 13 Ccellulose,±0.3‰ for δ 18 Ocellulose (1σ).<br />
4. Results <strong>and</strong> discussion<br />
4.1. Age-depth model, peat accumulation rate <strong>and</strong> <strong>Sphagnum</strong><br />
peat stratigraphy<br />
The 14 C results which are given <strong>in</strong> Table 1 were used for the agedepth<br />
model of the “Dürres Maar” record (Fig. 3). All 14 Cresultswere<br />
calibrated <strong>and</strong> visualised us<strong>in</strong>g Oxcal (Bronk Ramsey, 1995, 2008).<br />
The bottom of the record was dated to ∼4000 cal. yr BP. Peat growth<br />
<strong>in</strong> the follow<strong>in</strong>g two millennia was ~0.9 mm/yr. A considerable<br />
<strong>in</strong>crease <strong>in</strong> the peat accumulation rate occurs at a depth of ~5.2 m<br />
(∼350 AD). With<strong>in</strong> the follow<strong>in</strong>g ∼700 years about 3.5 m peat<br />
accumulated with a very constant accumulation rate, which means a<br />
growth of 5 cm per decade <strong>and</strong> temporal resolution of two years per<br />
cm (5.3 mm/yr). A decrease <strong>in</strong> the accumulation rate is obvious at<br />
~1.5 m. This change is moderate compared to the change <strong>in</strong> the lower<br />
part of the peat deposit <strong>and</strong> causes a reduction <strong>in</strong> the peat<br />
accumulation rate to ~1.7 mm/yr dur<strong>in</strong>g the uppermost ∼130 cm of<br />
the deposit.<br />
Fig. 3. Lithology <strong>and</strong> age-depth-model of the “Dürres Maar” peat deposit. R_Date values represent mean depths of the <strong>in</strong>dividual samples used for AMS 14 C measurements.
Most of the “Dürres Maar” record consists of weakly decomposed<br />
<strong>Sphagnum</strong> peat. A section of peat with somewhat higher decomposition<br />
appears between 65–85 cm <strong>and</strong> particularly <strong>in</strong> the deeper part of<br />
the record below ~570 cm (Fig. 3). The observed change <strong>in</strong> peat<br />
decomposition at ∼570 cm corresponds well with the <strong>in</strong>itial<br />
appearance of an Eriophorum spec. dom<strong>in</strong>ated peat section with a<br />
thickness of ~30 cm where <strong>Sphagnum</strong> is present only <strong>in</strong> very small<br />
amounts. This section is followed by a hiatus of ∼26 cm. Below the<br />
hiatus <strong>Sphagnum</strong> aga<strong>in</strong> is the dom<strong>in</strong>ant peat form<strong>in</strong>g component. In<br />
this deeper part of the record the preservation status of s<strong>in</strong>gle<br />
<strong>Sphagnum</strong> plants is, however, considerably weaker than above<br />
∼570 cm.<br />
R. Moschen et al. / Chemical Geology 259 (2009) 262–272<br />
Four small sections conta<strong>in</strong>ed very watery peat with no or too little<br />
<strong>sub</strong>stance to be sampled lead<strong>in</strong>g to <strong>in</strong>terruptions of the taken core.<br />
Interruptions are at 286–300 cm, 334–342 cm, 382–390 cm, 448–<br />
452 cm, <strong>and</strong> the described Hiatus of ∼26 cm at 600–626 cm (Fig. 3).<br />
4.2. <strong>Sphagnum</strong> assemblages<br />
From the bog's surface to a depth of approximately 60 cm the peat<br />
predom<strong>in</strong>antly consists of scarcely decomposed <strong>Sphagnum</strong> magellanicum<br />
(Table 2). This taxon was described to become dom<strong>in</strong>ant <strong>in</strong><br />
many raised bogs <strong>in</strong> northeast Europe dur<strong>in</strong>g the last millennium<br />
(Mauquoy <strong>and</strong> van Geel, 2007). Below this level a th<strong>in</strong> Eriophorum<br />
Table 2<br />
Results of <strong>Sphagnum</strong> species identification us<strong>in</strong>g a weighted-averag<strong>in</strong>g ord<strong>in</strong>ation technique employed on prist<strong>in</strong>e samples of <strong>Sphagnum</strong> branches<br />
Depths [cm] S. section Acutifolia <strong>Sphagnum</strong> cuspidata <strong>Sphagnum</strong> palustre <strong>Sphagnum</strong> magellanicum Non-identifiable ∑<br />
20–22 1 11 12<br />
36–38 4 1 7 12<br />
52–54 2 2 8 12<br />
68–70 11 1 12<br />
84–86 Eriophorum dom<strong>in</strong>ated peat (almost no <strong>Sphagnum</strong> branches or branch fragments preserved)<br />
100–102 Eriophorum dom<strong>in</strong>ated peat (almost no <strong>Sphagnum</strong> branches or branch fragments preserved)<br />
116–118 12 12<br />
132–134 11 1 12<br />
148–150 11 1 12<br />
164–166 10 2 12<br />
172–174 9 2 1 12<br />
180–182 12 12<br />
188–190 11 1 12<br />
200–202 12 12<br />
212–214 12 12<br />
228–230 12 12<br />
244–246 11 1 12<br />
252–254 12 12<br />
268–270 12 12<br />
276–278 11 1 12<br />
280–282 11 1 12<br />
308–310 12 12<br />
324–326 12 12<br />
330–332 12 12<br />
350–352 12 12<br />
364–366 11 1 12<br />
380–382 12 12<br />
396–398 12 12<br />
404–406 12 12<br />
412–414 12 12<br />
428–430 12 12<br />
436–438 12 12<br />
444–446 12 12<br />
460–462 11 1 12<br />
476–478 12 12<br />
492–494 11 1 12<br />
516–518 11 1 12<br />
524–526 12 12<br />
540–542 10 2 12<br />
558–560 Eriophorum dom<strong>in</strong>ated peat (almost no <strong>Sphagnum</strong> branches or branch fragments preserved)<br />
572–574 Eriophorum dom<strong>in</strong>ated peat (almost no <strong>Sphagnum</strong> branches or branch fragments preserved)<br />
576–580 Eriophorum dom<strong>in</strong>ated peat (almost no <strong>Sphagnum</strong> branches or branch fragments preserved)<br />
580–582 Eriophorum dom<strong>in</strong>ated peat (almost no <strong>Sphagnum</strong> branches or branch fragments preserved)<br />
588–590 Eriophorum dom<strong>in</strong>ated peat (almost no <strong>Sphagnum</strong> branches or branch fragments preserved)<br />
592–594 Eriophorum dom<strong>in</strong>ated peat (almost no <strong>Sphagnum</strong> branches or branch fragments preserved)<br />
628–630<br />
630–632<br />
636–638<br />
644–646<br />
5 7 12<br />
660–662<br />
668–670<br />
4 2 6 12<br />
676–678<br />
692–694<br />
4 8 12<br />
708–710<br />
716–718<br />
724–726<br />
6 6 12<br />
From a depth of ∼630 cm onwards <strong>in</strong> most samples almost all branches were decomposed to s<strong>in</strong>gle leaves such that species identification becomes difficult or even impossible. When<br />
11 or even 12 branches could be related to section Acutifolia, the averaged statistical frequency of <strong>Sphagnum</strong> sect. Acutifolia with<strong>in</strong> the branch sample is 81% <strong>and</strong> 87%, respectively<br />
(bold figures) (81% confidence <strong>in</strong>terval: lower boundary 0.61%, upper boundary 100%; for the 87% <strong>in</strong>terval: lower boundary 0.73%, upper boundary 100%; confidence region: 95%).<br />
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268 R. Moschen et al. / Chemical Geology 259 (2009) 262–272<br />
peat section occurs which is <strong>sub</strong>sequently followed by a scarcely<br />
decomposed <strong>Sphagnum</strong> peat where the dom<strong>in</strong>ant moss is <strong>Sphagnum</strong><br />
section Acutifolia (Table 2). The difficulty of an accurate identification<br />
of section Acutifolia to the species level poses problems <strong>in</strong> determ<strong>in</strong><strong>in</strong>g<br />
the microhabitat of the s<strong>in</strong>gle plants, s<strong>in</strong>ce this section <strong>in</strong>cludes<br />
hummock <strong>and</strong> lawn species. This is not a problem for <strong>Sphagnum</strong><br />
fuscum <strong>and</strong> <strong>Sphagnum</strong> capillifolium var. rubellum, s<strong>in</strong>ce both species<br />
occupy the same habitat, i.e. relatively dry hummocks <strong>and</strong> would,<br />
therefore, record the same environmental <strong>in</strong>formation (Andrus et al.,<br />
1983; Ryd<strong>in</strong> <strong>and</strong> McDonald, 1985; Janssens, 1992). The two Acutifolia<br />
species <strong>Sphagnum</strong> <strong>sub</strong>nitens <strong>and</strong> S. molle are, however, lawn species<br />
<strong>and</strong>, thus, would reduce the accuracy of any palaeoecological<br />
reconstruction based on stable <strong>isotopes</strong> from plant material identified<br />
to <strong>Sphagnum</strong> section Acutifolia alone (Mauquoy <strong>and</strong> van Geel, 2007).<br />
Presence of <strong>Sphagnum</strong> fuscum <strong>and</strong> the two lawn species S. <strong>sub</strong>nitens<br />
<strong>and</strong> S. molle <strong>in</strong> the “Dürres Maar” peat deposit is, however, rather<br />
unlikely. In a number of fresh collections from a transect through the<br />
bogs centre, dom<strong>in</strong>at<strong>in</strong>g microscopically exam<strong>in</strong>ed elements are<br />
<strong>Sphagnum</strong> magellanicum <strong>and</strong> S. capillifolium var. rubellum (Forst<br />
et al., 1997). <strong>Sphagnum</strong> fuscum, S. <strong>sub</strong>nitens <strong>and</strong> S. molle are neither<br />
present <strong>in</strong> the current vegetation cover of peat bogs of the Westeifel<br />
Volcanic Field nor described <strong>in</strong> palaeobotanical <strong>in</strong>vestigations on peat<br />
deposits of this region (Straka, 1975; Forst et al., 1997). Towards a<br />
contribution of lawn species of section Acutifolia, moreover, argues<br />
that dry hummocks tend to persist <strong>in</strong> the same location over millennia<br />
rather than alternat<strong>in</strong>g with hollows hold<strong>in</strong>g wetter conditions<br />
(Barber, 1981; Charman, 2002). Additionally, the presence of S. molle<br />
most likely could be ruled out on ground of the overall rarity of this<br />
species <strong>in</strong> north-western Europe (Barber, 1981; Frahm <strong>and</strong> Frey, 2004).<br />
We, therefore, assume that between ∼60 <strong>and</strong> ∼550 cm the peat<br />
deposit predom<strong>in</strong>antly consists of <strong>Sphagnum</strong> capillifolium var.<br />
rubellum.<br />
From a depth of ∼550 cm onwards the peat decomposition<br />
considerably <strong>in</strong>creases <strong>and</strong> <strong>Sphagnum</strong> species identification becomes<br />
much more difficult or even impossible. Between ∼550 <strong>and</strong> ∼600 cm a<br />
second Eriophorum dom<strong>in</strong>ated peat section with very small amounts<br />
of <strong>Sphagnum</strong> occurs. The <strong>in</strong>dividual samples of this section neither<br />
conta<strong>in</strong> preserved <strong>Sphagnum</strong> branches nor branch fragments. Species<br />
identification of <strong>Sphagnum</strong> branches on the basis of the characteristic<br />
hyal<strong>in</strong>e cells of the s<strong>in</strong>gle leaves, thus, could not be accomplished.<br />
Below this second Eriophorum peat section which is followed by the<br />
described hiatus of ∼26 cm, <strong>Sphagnum</strong> becomes the dom<strong>in</strong>at<strong>in</strong>g<br />
genus aga<strong>in</strong>. Due to the <strong>in</strong>creased peat decomposition at this deeper<br />
part of the profile the predom<strong>in</strong>ant number of <strong>Sphagnum</strong> branches<br />
were, however, decomposed to s<strong>in</strong>gle leaves <strong>in</strong> most of the samples.<br />
Thus, from a depth of ∼550 cm onwards species identification was<br />
overall limited. Few samples from this section conta<strong>in</strong> several<br />
preserved branches <strong>and</strong> branch fragments. The small <strong>and</strong> very delicate<br />
<strong>in</strong>dividual <strong>Sphagnum</strong> leaves of these branches were, however,<br />
frequently deteriorated so strongly that valid species identification<br />
could not be accomplished <strong>in</strong> all cases (Table 2). As stated above,<br />
between ∼60 <strong>and</strong> ∼550 cm we are predom<strong>in</strong>antly deal<strong>in</strong>g with<br />
<strong>Sphagnum</strong> capillifolium var. rubellum. It is therefore likely that the nonidentifiable<br />
branches from the <strong>in</strong>dividual samples from greater depths<br />
of the record orig<strong>in</strong>ate at least partly from <strong>Sphagnum</strong> capillifolium.<br />
Two branches of <strong>Sphagnum</strong> palustre at a depth of 660–662 cm,<br />
however, po<strong>in</strong>t to admixture of other <strong>Sphagnum</strong> species (Table 2).<br />
Importantly, <strong>in</strong>dependent from the success <strong>in</strong> <strong>Sphagnum</strong> species<br />
identification, almost all of the samples from the deeper part of the<br />
profile with <strong>in</strong>creased peat decomposition do neither conta<strong>in</strong><br />
branches nor branch fragments <strong>in</strong> an adequate amount for cellulose<br />
extraction <strong>and</strong> stable isotope measurements.<br />
In contrast, the number of stem sections was sufficient <strong>in</strong> the core<br />
section with higher peat decomposition because <strong>Sphagnum</strong> stems are<br />
much more resistant to decomposition than <strong>Sphagnum</strong> branches.<br />
Thus, it is possible to separate s<strong>in</strong>gle physical components clearly<br />
relatable to the genius <strong>Sphagnum</strong> for stable isotope analysis. On the<br />
other h<strong>and</strong>, <strong>Sphagnum</strong> species identification is impossible if only stem<br />
sections are preserved <strong>and</strong> would reduce the accuracy of palaeoecological<br />
reconstructions based on stable <strong>isotopes</strong>. This implies that it<br />
might be extremely difficult, if not impossible, to derive samples of<br />
s<strong>in</strong>gle <strong>Sphagnum</strong> species from bulk peat material for stable isotope<br />
measurements if the decomposition status of the peat under<br />
<strong>in</strong>vestigation is considerably high.<br />
4.3. <strong>Stable</strong> <strong>carbon</strong> isotopic composition of <strong>Sphagnum</strong> cellulose<br />
The stable <strong>carbon</strong> isotope ratios of cellulose extracted from the<br />
different physical components of <strong>Sphagnum</strong> plants from the “Dürres<br />
Maar” record are <strong>in</strong> the same range as δ 13 Ccellulose values reported <strong>in</strong><br />
previous studies on peat records spann<strong>in</strong>g the last few millennia (e.g.<br />
Hong et al., 2001; Pancost et al., 2003; Jędrysek <strong>and</strong> Skrzypek, 2005).<br />
These studies, however, were accomplished on cellulose derived from<br />
bulk peat material. In the “Dürres Maar” record, we found significant<br />
stable <strong>carbon</strong> isotopic offset between the cellulose extracted from<br />
<strong>Sphagnum</strong> branches <strong>and</strong> the cellulose extracted from <strong>Sphagnum</strong> stem<br />
sections with significantly heavier δ 13 C cellulose values for the branches<br />
than those of the stems (Fig. 4). The observed isotopic offset between<br />
the δ 13 C cellulose values of <strong>Sphagnum</strong> branches <strong>and</strong> stem sections<br />
averages to 1.5‰, exhibits a strong degree of correlation (r 2 =0.73,<br />
n=41) <strong>and</strong> is statistically highly significant (P-value for t-unpaired test<br />
0.02, significance levelb0.0001).<br />
The isotopic offset is clearly observable down-core, however, the<br />
offset is presumably not consistent through time. The results obta<strong>in</strong>ed<br />
po<strong>in</strong>t to a decrease <strong>in</strong> the isotopic offset between branches <strong>and</strong> stem<br />
sections with <strong>in</strong>creas<strong>in</strong>g age of the plant material (Fig. 6). S<strong>in</strong>ce the<br />
record of <strong>Sphagnum</strong> branches conta<strong>in</strong>s several gaps compared to the<br />
record of stem sections at greater depth, no clear evidence for a<br />
decrease <strong>in</strong> the isotopic offset between branches <strong>and</strong> stem sections<br />
could be deduced from our results. Below the Eriophorum dom<strong>in</strong>ated<br />
peat eleven δ 13 C cellulose values could be obta<strong>in</strong>ed from stem sections.<br />
From the same core sequence branches from solely four samples could<br />
be separated <strong>in</strong> an adequate amount to provide enough plant material<br />
for stable isotope measurements s<strong>in</strong>ce branch deterioration <strong>in</strong>creases<br />
down-core (Fig. 4). Nevertheless, our results <strong>in</strong>dicate to a decrease <strong>in</strong><br />
the δ 13 Ccellulose offset between <strong>Sphagnum</strong> branches <strong>and</strong> stem sections<br />
with <strong>in</strong>creas<strong>in</strong>g peat decomposition. We can only speculate that the<br />
relatively fast deterioration of <strong>Sphagnum</strong> branches compared to the<br />
much higher stability of <strong>Sphagnum</strong> stems causes a somewhat faster<br />
degradation of the plant cellulose <strong>in</strong> the branches <strong>in</strong> contrast to more<br />
moderate cellulose degradation <strong>in</strong> the stems.<br />
As stated before, from approximately 60 cm to a depth of ∼550 cm<br />
the peat deposit most likely consist ma<strong>in</strong>ly of <strong>Sphagnum</strong> capillifolium<br />
var. rubellum (Table 2). This species forms dry hummocks <strong>and</strong> is<br />
relatively sensitive to changes <strong>in</strong> bog wetness (Ménot-Combes et al.,<br />
2002). In a raised bog hummock-microhabitat, water availability is<br />
most likely better for closely-packed <strong>Sphagnum</strong> stems situated with<strong>in</strong><br />
the moss tissue, than on top of the hummock where recently grown<br />
branches of the plant's capitulae are exposed to higher solar radiation<br />
<strong>and</strong>, therefore, to higher evaporation. Adequate water availability<br />
with<strong>in</strong> the hummock leads to well filled hyal<strong>in</strong>e cells limit<strong>in</strong>g the<br />
diffusion of CO 2 to the chloroplasts of the <strong>Sphagnum</strong> stems. The<br />
δ 13 Ccellulose value of these stems, thus, is <strong>in</strong>fluenced by reduced<br />
fractionation aga<strong>in</strong>st the heavier 13 CO 2 due to the reduced supply of<br />
CO2. Compared to the situation with<strong>in</strong> the shielded hummock, dur<strong>in</strong>g<br />
the grow<strong>in</strong>g season the recently grown branches which form the<br />
plant's capitulae are frequently relatively dry. Hyal<strong>in</strong>e cells are less<br />
filled <strong>and</strong> the water reservoir surround<strong>in</strong>g the branches' chloroplasts<br />
is relatively small result<strong>in</strong>g <strong>in</strong> enlarged CO2 diffusion <strong>and</strong> simultaneously<br />
<strong>in</strong>creased fractionation aga<strong>in</strong>st the heavier 13 CO 2. Hence,<br />
differences <strong>in</strong> water availability can be assumed to cause an isotopic<br />
offset between branches <strong>and</strong> stem sections.
Fig. 4. (A) Comparison of the stable <strong>carbon</strong> isotope composition of cellulose derived<br />
from <strong>Sphagnum</strong> branches (black diamonds) <strong>and</strong> <strong>Sphagnum</strong> stem sections (grey<br />
triangles) manually separated from <strong>in</strong>dividual bulk peat samples from the “Dürres<br />
Maar” record. The overall precision of replicate analyses is better than±0.1‰. No error<br />
bars are added to the symbols, s<strong>in</strong>ce the error bars are smaller than the symbol size.<br />
(B) Scatter plot of stem δ 13 C cellulose <strong>and</strong> branch δ 13 C cellulose demonstrat<strong>in</strong>g the strong<br />
relationship between the stable <strong>carbon</strong> isotope values of the different physical plant<br />
components.<br />
Accord<strong>in</strong>g to this consideration differences <strong>in</strong> stable <strong>carbon</strong> isotope<br />
fractionation of <strong>Sphagnum</strong> stems <strong>and</strong> branches should result <strong>in</strong> relatively<br />
high δ 13 Ccellulose values of the stems <strong>in</strong> contrast to lower δ 13 Ccellulose<br />
values of the branches. The isotopic offset between branches <strong>and</strong> stem<br />
sections, however, shows an opposite behaviour (Fig. 4). The branch<br />
δ 13 C cellulose values are significantly enriched compared to the δ 13 C cellulose<br />
values of the stem sections. The reason for this offset cannot be seen as a<br />
reflection of the water barrier surround<strong>in</strong>g the chloroplasts of the<br />
different physical plant components.<br />
Therefore, factors other than the balance between <strong>in</strong>creas<strong>in</strong>g<br />
conductance to CO2 <strong>and</strong> the decreas<strong>in</strong>g assimilation capacity which is<br />
clearly relatable to the water availability must control the observed<br />
stable <strong>carbon</strong> isotopic offset. The cause for the isotopic offset is,<br />
however, difficult to expla<strong>in</strong>. Reasonable hypotheses could be seen <strong>in</strong><br />
R. Moschen et al. / Chemical Geology 259 (2009) 262–272<br />
the growth of <strong>Sphagnum</strong> branches <strong>and</strong> stems dur<strong>in</strong>g different time<br />
spans of the grow<strong>in</strong>g season, the dimension <strong>and</strong> accessibility of the<br />
chloroplasts of branches <strong>and</strong> stems for atmospheric CO2, differences <strong>in</strong><br />
the water use efficiency of branches <strong>and</strong> stems, <strong>and</strong> a different<br />
susceptibility of these different physical plant components to<br />
desiccation effects, <strong>in</strong>fluenc<strong>in</strong>g the rate of photosynthesis (Schleser,<br />
1992; Williams <strong>and</strong> Flanagan, 1996; Rice, 2000; Ménot <strong>and</strong> Burns,<br />
2001; Loader et al., 2007). Such hypotheses could, however, solely be<br />
clarified due to <strong>sub</strong>stantial plant-physiological <strong>in</strong>vestigations not<br />
performed on <strong>Sphagnum</strong> so far.<br />
4.4. Oxygen isotopic composition of <strong>Sphagnum</strong> cellulose<br />
Comparable to the results obta<strong>in</strong>ed for δ 13 Ccellulose, the <strong>oxygen</strong><br />
isotopic composition of cellulose separately extracted from <strong>Sphagnum</strong><br />
branches <strong>and</strong> stem sections reveal, that there also exist significant<br />
Fig. 5. (A) Comparison of the <strong>oxygen</strong> isotope composition of cellulose derived from<br />
<strong>Sphagnum</strong> branches (black diamonds) <strong>and</strong> <strong>Sphagnum</strong> stem sections (grey triangles)<br />
manually separated from <strong>in</strong>dividual bulk peat samples from the “Dürres Maar” record.<br />
Error bars represent ± 1 st<strong>and</strong>ard deviation (sd − 1 ) of the isotopic measurements of each<br />
sample (n =2–3). (B) Scatter plot of stem δ 18 Ocellulose <strong>and</strong> branch δ 18 Ocellulose<br />
demonstrat<strong>in</strong>g the strong relationship between the <strong>oxygen</strong> isotope values of the<br />
different physical plant components.<br />
269
270 R. Moschen et al. / Chemical Geology 259 (2009) 262–272<br />
Fig. 6. (A) Isotopic offset [‰] between the stable <strong>carbon</strong> isotopic values of cellulose<br />
derived from <strong>Sphagnum</strong> branches <strong>and</strong> stem sections (gray diamonds) <strong>and</strong> (B) between<br />
the <strong>oxygen</strong> isotopic values of cellulose derived from <strong>Sphagnum</strong> branches <strong>and</strong> stem<br />
sections (open triangles). Note the decrease <strong>in</strong> the stable <strong>carbon</strong> isotopic offset with<br />
<strong>in</strong>creas<strong>in</strong>g age of the plant material. The overall <strong>oxygen</strong> isotopic offset is smaller,<br />
however, consistent <strong>in</strong> time.<br />
<strong>oxygen</strong> isotopic offset between the different physical plant components.<br />
Fig. 5 shows that the δ 18 O cellulose values of the <strong>Sphagnum</strong><br />
branches are significantly heavier than those of the stem sections. The<br />
observed average offset of 0.9‰ exhibits almost the same strong<br />
correlation (r 2 =0.72, n=41) <strong>and</strong> is also statistically highly significant<br />
(P-value for t-unpaired test 0.06, significance levelb0.0001). The<br />
isotopic difference between the two plant components is, however,<br />
less pronounced than the difference <strong>in</strong> the <strong>carbon</strong> isotopic composition<br />
(Figs. 4 <strong>and</strong> 5). Most <strong>in</strong>terest<strong>in</strong>gly, <strong>in</strong> contrast to the results<br />
obta<strong>in</strong>ed for δ 13 Ccellulose, the <strong>oxygen</strong> isotopic offset is consistent<br />
through time (Fig. 6).<br />
In general the <strong>oxygen</strong> isotopic composition of plant cellulose is<br />
controlled by (i) the isotopic composition of source water, (ii) the<br />
enrichment of the heavier isotope <strong>in</strong> leaf water due to evapotranspiration,<br />
<strong>and</strong> (iii) the overall biochemical fractionation between source<br />
water <strong>and</strong> plant cellulose (Brenn<strong>in</strong>kmeijer et al., 1982). In raised bog<br />
hummock-microhabitats, water availability is most likely better for<br />
closed-packed <strong>Sphagnum</strong> stems situated with<strong>in</strong> the hummock, than<br />
on the moss surface, were recently grown branches of the moss<br />
capitulae are exposed to high evaporation. Water taken up by capillary<br />
water movement <strong>in</strong> <strong>Sphagnum</strong> mats orig<strong>in</strong>ates at least partially from<br />
precipitation <strong>and</strong> to a higher amount from water from below 20–<br />
30 cm, which has been found to be much more isotopically<br />
homogenous than surface water (Ménot-Combes et al., 2002).<br />
Enlarged evaporation from <strong>Sphagnum</strong> capitulae which consist of<br />
recently grown branches should, therefore, result <strong>in</strong> enriched δ 18 O<br />
values of the rema<strong>in</strong><strong>in</strong>g water, lead<strong>in</strong>g to enriched δ 18 O values of the<br />
branch cellulose. In the “Dürres Maar” record the isotopic offset<br />
between branches <strong>and</strong> stem sections po<strong>in</strong>t to such behaviour, s<strong>in</strong>ce<br />
the δ 18 Ocellulose values of the branches are significantly enriched<br />
compared to the δ 18 O cellulose values of the stem sections (Fig. 5).<br />
Accord<strong>in</strong>g to this consideration the <strong>oxygen</strong> isotopic offset between<br />
branches <strong>and</strong> stem sections is presumably caused by differences <strong>in</strong> the<br />
<strong>oxygen</strong> isotopic composition of the water which is available for<br />
cellulose synthesis at the two different physical components of the<br />
<strong>Sphagnum</strong> plants. Such hypothesis is <strong>sub</strong>stantiated by the f<strong>in</strong>d<strong>in</strong>g,<br />
that dur<strong>in</strong>g field <strong>and</strong> laboratory exam<strong>in</strong>ations, evaporation rates have<br />
shown to be higher above mosses than over st<strong>and</strong><strong>in</strong>g surface waters<br />
(Nichols <strong>and</strong> Brown, 1980; Ménot-Combes et al., 2002). This effect can<br />
be seen as a result of the high leave to surface area presented by<br />
mosses. The specific plant physiology allows rapid evaporation from<br />
<strong>Sphagnum</strong> covered locations most likely result<strong>in</strong>g <strong>in</strong> enriched <strong>oxygen</strong><br />
isotopic values of the water available for cellulose synthesis at the<br />
plants crown, i.e. recently grown branches <strong>and</strong> the plants capitulae.<br />
The down core differences <strong>in</strong> the <strong>oxygen</strong> isotope composition of<br />
branches <strong>and</strong> stem sections are relatively small <strong>and</strong> variable but<br />
statistically highly significant. The offset suggest that different plants<br />
are respond<strong>in</strong>g similarly to the <strong>oxygen</strong> isotopic composition of the<br />
source water available for cellulose synthesis <strong>and</strong> that multiple plants<br />
record the isotopic composition of their source water <strong>in</strong> a similar<br />
manner. This is a fundamental implication for palaeoclimatic<br />
reconstructions us<strong>in</strong>g the δ 18 O cellulose value of <strong>Sphagnum</strong> cellulose <strong>in</strong><br />
order to reconstruct hydrological conditions of peat bogs <strong>in</strong> regard to<br />
the isotopic composition of bog waters. The systematic <strong>oxygen</strong> isotope<br />
offset between <strong>Sphagnum</strong> branches <strong>and</strong> stems, however, suggest that<br />
removal of all non-<strong>Sphagnum</strong> plants or plant fragments is no adequate<br />
approach to deduce potential changes <strong>in</strong> the hydrological conditions<br />
by means of <strong>oxygen</strong> <strong>isotopes</strong>.<br />
5. Implications for climate reconstructions<br />
Our results displays that palaeoclimate <strong>in</strong>terpretations based on<br />
cellulose stable isotope values derived from peat archives must take<br />
<strong>in</strong>to account that there exist significant stable <strong>carbon</strong> <strong>and</strong> <strong>oxygen</strong><br />
isotopic offset between cellulose from <strong>Sphagnum</strong> branches <strong>and</strong> stems.<br />
The results <strong>in</strong>dicate that the use of bulk peat material without respect<br />
to the observed differences between the isotopic composition of<br />
<strong>Sphagnum</strong> branches <strong>and</strong> stems could clearly lead to erroneous<br />
<strong>in</strong>terpretations of isotope records, even if the peat predom<strong>in</strong>antly<br />
consists of <strong>Sphagnum</strong>. Assum<strong>in</strong>g down-core changes <strong>in</strong> the ratio of<br />
branches to stem sections <strong>in</strong> <strong>Sphagnum</strong> peat deposits, Table 3 allows<br />
Table 3<br />
Approximation of the <strong>in</strong>fluence of a chang<strong>in</strong>g ratio between <strong>Sphagnum</strong> branches <strong>and</strong><br />
stems on a stable <strong>carbon</strong> isotopic value of a bulk <strong>Sphagnum</strong> peat sample<br />
<strong>Sphagnum</strong> branches <strong>and</strong> stems Bulk <strong>Sphagnum</strong><br />
Given δ 13 Cbranch cellulose value Branch/stem-ratio Resultant δ 13 Cbulk cellulose value<br />
−24.00‰ vs. V-PDB 1:1 −24.74‰ vs. V-PDB<br />
Reduction of 10% of branches 0.9:1 −24.77‰<br />
20% 0.8:1 −24.82‰<br />
30% 0.7:1 −24.87‰<br />
40% 0.6:1 −24.92‰<br />
50% 0.5:1 −24.98‰<br />
60% 0.4:1 −25.05‰<br />
70% 0.3:1 −25.13‰<br />
80% 0.2:1 −25.23‰<br />
90% 0.1:1 −25.34‰<br />
100% 0:1 −25.47‰<br />
Due to the observed mean offset of 1.47‰, a hypothetic stable <strong>carbon</strong> isotope value of<br />
branch cellulose of −24.00‰ results <strong>in</strong> a stable <strong>carbon</strong> isotope value of a bulk peat<br />
sample of approximately −24.74‰ if the ratio of <strong>Sphagnum</strong> branches <strong>and</strong> stem section is<br />
1:1 (−24.00‰+1/2 offset=bulk). S<strong>in</strong>ce the st<strong>and</strong>ard deviation of the stable <strong>carbon</strong><br />
isotope measurements is better than±0.1‰ (1σ), a reduction of the branch/stem ratio to<br />
less than approximately 0.6:1 would cause a significant shift <strong>in</strong> the stable <strong>carbon</strong><br />
isotope ratio of a δ 13 C bulk cellulose value towards the 13 C depleted stem isotope signal.
estimat<strong>in</strong>g the <strong>in</strong>fluence of a chang<strong>in</strong>g ratio between branches <strong>and</strong><br />
stems on bulk peat stable <strong>carbon</strong> isotopic records derivable from such<br />
deposits. Based on an evenly distributed amount of branches <strong>and</strong><br />
stems, i.e. 50% branches <strong>and</strong> 50% stems represent<strong>in</strong>g a ratio of 1:1, a<br />
reduction of the ratio between branches <strong>and</strong> stem to less than<br />
approximately 0.6:1 would cause a significant shift <strong>in</strong> the stable<br />
<strong>carbon</strong> isotope ratio of a δ 13 Cbulk peat value towards the 13 C depleted<br />
stem isotope signal. S<strong>in</strong>ce even larger down-core changes of the<br />
branches to stem ratio could not be ruled out, remov<strong>in</strong>g the plant<br />
material other than <strong>Sphagnum</strong> is not sufficient for produc<strong>in</strong>g reliable<br />
stable isotope series. Thus, on the scale of a reliable <strong>in</strong>terpretation of<br />
stable isotope records from <strong>Sphagnum</strong> peat deposits it seems essential<br />
to conf<strong>in</strong>e sampl<strong>in</strong>g to either branches or stem sections of <strong>Sphagnum</strong><br />
or even to sample both plant components separately.<br />
It has been shown that the amplitude of the isotopic response of<br />
<strong>Sphagnum</strong> cellulose to environmental condition is presumably species<br />
dependent (Ménot <strong>and</strong> Burns, 2001; Ménot-Combes et al., 2002).<br />
Palaeoclimate studies based on cellulose stable isotope values derived<br />
from peat archives must take <strong>in</strong>to consideration that valid species<br />
identification of preserved <strong>Sphagnum</strong> branches down-core is achievable<br />
solely if the profile under exam<strong>in</strong>ation consists of scarcely<br />
decomposed peat. Our results confirm that the separate sampl<strong>in</strong>g of<br />
<strong>Sphagnum</strong> branches <strong>and</strong> stem sections seems unrealistic when data<br />
sets have to be produced over long time periods, because <strong>in</strong> most<br />
<strong>in</strong>stances peat decomposition progresses over time. The much higher<br />
resistance of stems to peat decomposition, however, allows separat<strong>in</strong>g<br />
these plant components which can be clearly determ<strong>in</strong>ed as <strong>Sphagnum</strong>.<br />
Consequently, it seems promis<strong>in</strong>g to sample solely stem sections<br />
to derive palaeoclimate <strong>in</strong>formation from the peat record on the basis<br />
of stable <strong>isotopes</strong>. The relatively large <strong>Sphagnum</strong> stems have the<br />
additional advantage that their sampl<strong>in</strong>g is not as time consum<strong>in</strong>g as<br />
pick<strong>in</strong>g a sufficient amount of branches or even branch fragments.<br />
That way, any <strong>in</strong>fluence of the stable isotopic offsets between<br />
branches <strong>and</strong> stems on changes between the fraction of braches <strong>and</strong><br />
stems of <strong>in</strong>dividual bulk peat samples could be ruled out.<br />
On the other h<strong>and</strong>, identification of <strong>Sphagnum</strong> species is<br />
impossible on the basis of stem sections. Because raised bogs are<br />
composed of a variety of different microhabitats with a pattern of<br />
different <strong>Sphagnum</strong> species, shifts <strong>in</strong> the <strong>Sphagnum</strong> assemblages<br />
down core could not be categorically ruled out. S<strong>in</strong>ce the amplitude of<br />
any stable isotope response signal of <strong>Sphagnum</strong> cellulose is presumably<br />
species dependent (Ménot <strong>and</strong> Burns, 2001; Ménot-Combes<br />
et al., 2002), such changes <strong>in</strong> the species composition could easily<br />
cause mis<strong>in</strong>terpretations of the isotopic records <strong>and</strong> thus may lead to<br />
systematic errors when us<strong>in</strong>g such records for palaeoclimate<br />
reconstructions.<br />
6. Conclusions<br />
The stable <strong>carbon</strong> <strong>and</strong> <strong>oxygen</strong> isotope ratios of cellulose extracted<br />
separately from <strong>Sphagnum</strong> branches <strong>and</strong> stem sections from the<br />
“Dürres Maar” record reveal that there exist significant isotopic offset<br />
between these two different physical plant components. Isotopic<br />
differences are relatively small, however, both offsets exhibits a strong<br />
degree of correlation <strong>and</strong> are statistically highly significant. Our<br />
results <strong>in</strong>dicate that the stable <strong>carbon</strong> isotopic offset between<br />
branches <strong>and</strong> stem sections presumably decreases with <strong>in</strong>creas<strong>in</strong>g<br />
age of the plant material. In contrast, the <strong>oxygen</strong> isotopic offset is less<br />
pronounced, however, consistent <strong>in</strong> time.<br />
The observed significant offsets between the stable <strong>carbon</strong> <strong>and</strong><br />
<strong>oxygen</strong> isotopic composition of <strong>Sphagnum</strong> branches <strong>and</strong> stem sections<br />
implies that if a physical differentiation of these components prior to<br />
stable isotope analyses is impossible, systematic mis<strong>in</strong>terpretations of<br />
stable isotope records are likely. This is because if bulk <strong>Sphagnum</strong><br />
material is used for stable isotope measurements, isotopic records<br />
comprise of two different signals: firstly, an environmental signal<br />
R. Moschen et al. / Chemical Geology 259 (2009) 262–272<br />
based on the plant response to external controls (presumably<br />
<strong>in</strong>clud<strong>in</strong>g temperature, relative humidity, light regime, <strong>and</strong> nutrient<br />
availability). This signal is, however, masked by a second plant<br />
physiological signal orig<strong>in</strong>at<strong>in</strong>g from the described isotopic offset<br />
between branches <strong>and</strong> stem sections of <strong>Sphagnum</strong>. S<strong>in</strong>ce down-core<br />
changes <strong>in</strong> the ratio of branches to stem sections are most likely, the<br />
removal of all non-<strong>Sphagnum</strong> plants or plant fragments is <strong>in</strong>sufficient<br />
to retrieve stable isotope signals exclusively reflect<strong>in</strong>g palaeoenvironmental<br />
conditions.<br />
Acknowledgements<br />
We thank Georg Heumann, Thomas Litt, Jörn Parplies, Nils Riedel<br />
<strong>and</strong> He<strong>in</strong>z Vos for assistance <strong>in</strong> the field. Sample storage was afforded<br />
by Christa Lankes from the Institute of Crop Science <strong>and</strong> Resource<br />
Conservation, Bonn, Germany. The help of Stefanie Wagner dur<strong>in</strong>g<br />
core sampl<strong>in</strong>g is greatly acknowledged. We wish to thank Bas van Geel<br />
for teach<strong>in</strong>g us <strong>in</strong> <strong>Sphagnum</strong> species identification from s<strong>in</strong>gle leaves<br />
on the basis of the characteristics of their hyal<strong>in</strong>e <strong>and</strong> chlorophyllose<br />
cells. Support from Harald Strauß from the Geologisch-Paläontologisches<br />
Institut und Museum, Westfälische Wilhelms-Universität<br />
Münster, Germany is also acknowledged. Cellulose extraction <strong>and</strong><br />
stable isotope measurements were carried out by Holger Wissel at the<br />
Institute of Chemistry <strong>and</strong> Dynamics of the Geosphere 4, Agrosphere.<br />
This work was supported by a grant of the Deutsche Forschungsgeme<strong>in</strong>schaft<br />
(German Research Foundation) to Robert Moschen (grant<br />
MO 1401/2-1).<br />
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