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Article

n-Alkane Distribution—A Paleovegetation Change Indicator during the Period from Late Glacial to Late Holocene on Russian Plain (Bryansk Region)

by
Ekaterina Stolpnikova
1,2,*,
Natalia Kovaleva
2 and
Ivan Kovalev
2
1
A.N. Severtsov Institute of Ecology and Evolution RAS, Leninskiy Prospekt, 33, 119071 Moscow, Russia
2
Faculty of Soil Science, Lomonosov Moscow State University, Leninskiye Gory, 1-12, GSP-1, 119991 Moscow, Russia
*
Author to whom correspondence should be addressed.
Geosciences 2020, 10(3), 86; https://doi.org/10.3390/geosciences10030086
Submission received: 16 January 2020 / Accepted: 28 January 2020 / Published: 26 February 2020
Browse Figures
Versions Notes

Abstract

:
Loess-paleosol series are well preserved in the south part of the Russian Plain. However, these sequences have a low number of studies on their organic matter, such as researches of isotope composition, n-alkane and other biomarkers. Thus, the purpose of the study was to reconstruct vegetation conditions from the Late Glacial to Late Holocene. We used the leaf wax-derived n-alkanes to detect vegetation evolution of the Bryansk Region. The stable carbon isotope composition of organic matter and pedogenic carbonates was carried out for the same aim. Three paleosols (of Lasko, Bølling-Allerød warmings and Holocene second humus horizons) and modern soils of different relief positions were investigated. n-Alkane distribution, as well as isotope composition indicates changes from grassy to woody vegetation during this period. The use of biomarkers such as n-alkanes helps to more clearly interpret isotopic data.

1. Introduction

The loess-soil series are well represented on the Russian Plain, particularly in the south and south-west, and reflect the Late Pleistocene climatic restructuring by numerous climatic oscillations near Pleistocene–Holocene boundary. Many researchers [1,2,3] have found that Late Valdai (~23−10 kyr BP, Wurm IV, Late Glacial) loess deposits in this region are heterogeneous and separated by humic or gley horizons (undeveloped soils) in many stratigraphic sections. These horizons are markers of regional climatic fluctuations between 17−10.2 kyr BP.
Despite the abundance of paleogeographic studies of the Late Pleistocene loess-paleosol series on the Russian Plain [1,4,5,6,7,8], there are currently no paleoreconstructions based on n-alkane distribution. Although similar studies have been carried out for modern soils that were interested in anthropogenic pollution [9,10].
The final stage of Wurm (Valdai) glaciation is a period of sharply continental climate on the East European Plain in Pleistocene history [11,12]. The icecap reached the line, passing sublatitudinally from Vilnius to Smolensk, further to the north-west to the Rybinsk Reservoir and across Lake Kubenskoe to the northeast [12]. The southern edge of the permafrost zone reached Rostov and Volgograd—46°−48° N while the thickness of permafrost at the latitude of Moscow was 300 m [11].
The organic matter of the Late Pleistocene loess-paleosol series is a well-known proxy of paleoclimatic information. At the same time, the low content of Pleistocene organic matter in interstadial soils creates difficulties during such kinds of research. In this case, the content and distribution of leaf wax n-alkanes, the isotopic composition of organic carbon and carbonates are more useful methods for paleovegetation reconstructions [13,14,15].
The isotopic composition of organic carbon and different chemical parameters allowed us to reconstruct the dominance of meadow hydromorphic landscapes during the interstadials Lasko (18–16 kyr BP) and Bølling-Allerød (12.4–10.9 kyr BP), which is presented in our previous research—but this is not consistent with the trend of widespread climate aridification in the Late Pleistocene [16]. The composition of n-alkanes makes it possible to clarify the features of biocenoses.
Aliphatic hydrocarbons with a carbon chain length of 16 to 34 atoms, despite their low content in the organic matter (OM) of soils [17], are convenient compounds for studying of the paleovegetation. n-Alkanes are one of the most hydrophobic organic molecules of the soil lipid fraction which allows them to form strong complexes with solid phase of the soil and limits their migration in solutions due to their low solubility in water [13]. Being products of biogenic synthesis, n-alkanes have not formed in the soil during intracellular and extracellular degradation of organic compounds [13]. Thus, the distribution in the soil and seasonal changes in the homological composition of alkanes can reflect the localization and dynamics of the transformation and stabilization of organic matter from the moment it enters the soil [13]. The main sources of n-alkanes in soils are the overground parts of plants, the root and bacterial biomass [18,19,20]. Unbranched alkanes with a long C–C chain provide the hydrophobic properties of leaf waxes and serve as the primary barrier of plants from environmental conditions, protecting the leaf from moisture loss by transpiration [21]. Long chain n-alkanes C21-34 are synthesized as a part of epicuticular waxes on the leaves of terrestrial plants, and are the most distinguishable and widely used plant biomarkers entering the soil with plant residues [22,23].
On the surface of the plant cuticle, lipids such as cutin and suberin are associated with other, less polar compounds-waxes. In the leaf waxes of terrestrial plants, n-alkanes with a chain length of C25-33 have maximum concentrations. Alkanes are localized in the litter and then enter the soil, where they are considered the most degradation-resistant component [13]. Plants usually produce a set of n-alkanes in accordance with a strict coefficient of the predominance of odd compounds and often with the dominance of one (two) specific homologs [22]. For example, for herbaceous plants, C31 predominates in the total spectrum of n-alkanes, for woody plants C29 and C27 [23]. The predominance of compounds with a shorter hydrocarbon chain (23−25) was studied in the Sphagnum mosses spectra [24,25]. The increase in the concentration of medium chain n-alkanes (C16-24) is associated with microbial activity [23,26]. The synthesis of hydrocarbons in microorganisms depends on environmental conditions that determine the pathways of physiological regulation. Gram-positive bacteria, such as Clostridium, produce intracellular hydrocarbons with a chain length of 11−35 carbon atoms with a predominance of medium chain (C18-27) or long chain compounds C25-35 [27,28]. The Gram-negative anaerobic bacteria sulfate-reducers—Desulfovibrio desulfuricans—also produce C11-35 hydrocarbons and more than 80% of their total content is C25–C35 n-alkanes [29,30,31]. Various systematic groups of microorganisms are characterized by a specific composition of the hydrocarbon fraction, for example, cyanobacteria are unique producers of 7- and 8-methyl-heptadecans, photosynthetic bacteria differ in the synthesis of cyclic hydrocarbons [32], and long-chain hydrocarbons dominate in fungi [33]. It is important to note that microorganism cells are characterized by a low content of hydrocarbons (not more than 10% of dry weight) [34].
Due to the linear structure with a small number of functional groups, n-alkanes are especially stable and long-lived molecules that can persist in the soil for thousands of years [24,35]. In the surface horizons, the main source of n-alkanes is the litter, which determines the composition and content of hydrocarbons. Moreover, the ratio of dominant hydrocarbon chains remains [23]. The mechanisms of the entry and transformation of n-alkanes in the lower horizons are not clearly covered in the literature. A large role in this regard is given to earthworms and microorganisms [17,36,37,38]. The spectrum of n-alkanes differs from that observed in the upper horizons: the proportion of medium chain (C17-24) and even compounds increases [17,22,38,39].
In the process of the decomposition of plant material by microorganisms, the total amount of hydrocarbons decreases, and the content of individual compounds with a specific chain length does not change significantly [23,40].
Aquatic plants are characterized by the lower content of long-chain alkanes (C27-33) in comparison with terrestrial ones [41]. The predominance of even alkanes over odd can indicate the degradation of organic matter over time [14]. The authors of another publication [10] discuss that the predominance of even alkanes indicates the contribution of microbial biomass. In this case, the proportion of medium-chain alkanes (< C25) also increases.
Thus, based on such strong conservation as described above, n-alkanes have been actively used as biomarkers of plant communities and climatic conditions in paleoreconstructions in recent decades.
Alkanes are found in modern and fossil plant materials [42,43], in soils [9,10,21,39], lacustrine sediments [44], peat sediments and peaty soils [25,40,45], marine sediments [46,47] as well as paleosols [13,41,48] and loess-paleosol serias [15,49].
The purpose of this study was to reconstruct the paleovegetation changes in the loess-paleosol series of the Bryansk region (Russia) during the transition from the Lasko and Bølling-Allerød warm periods (Late Pleistocene) to the Late Holocene using the method of n-alkanes distribution in organic matter of modern and paleosols.

2. Materials and Methods

Two investigated loess-sandy-paleosol sequences are located on the southeast part of the East European Plain (Bryansk region, Russia) in the place called Trubchevskoe Opolye (Figure 1). Trubchevskoe Opolye is situated on the high right bank of Desna River (the watershed of the rivers Desna and Sudost) and represented by a landscape typical for Russian Plain with a paleocryogenic microrelief [8,50]. The study area is covered by a system of micro-elevations and micro-depressions (Figure 2a,b), which can reach a diameter of 5–10 m and depth up to 30 cm. An important feature of these landscapes is the presence of second humus horizons in the soils of micro-depressions at depths of 50-80 cm and the absence of such horizons at micro-elevations.
The average annual temperature in the study area is +5.4 °C. The amount of precipitation ranges from 550 to 590 mm [50]. Native soils for this region (right bank of Desna)—are gray forest soils under broadleaf forests of the forest-steppe zone (WRB: Albic Luvisols/Grey Luvic Phaeozems), but now these soils have almost all been plowed up and are called agrogrey soils.
Also, the original feature of the investigated area is formation of different subtypes of soils associated with positions in microrelief: varieties with the second humus horizon are formed in plate-shaped micro-depressions; gleyic variants are formed in the middle parts of slopes and gley ones—at the footslopes and deeper depressions. The systems of micro-depressions and micro-elevations are well traced in the walls of the quarries Krasnoe and Telec on the right bank of the Desna River (Figure 2a). Second humus horizons were indicated in micro-depression and depression of relief at the depth range 50–85 (Ab, Location 2 in Table A1 and Figure 2c) and 40–64 cm respectively (Ab, Location 3, Table A1).
The sample points (52°33′70′′ N, 33°42′62′′ E and (52°34′51′′ N, 33°44′71′′ E) of loess-paleosol series are located near villages Krasnoe and Telec, respectively (Figure 1). The soil profiles of micro-depression and micro-elevation located above the loess-soil series of quarries were sampled at altitudes of 182 and 175 m, respectively. Additionally, a profile of unplowing soil in a deeper depression was taken (altitude 142 m, Location 3 in Table A1, Table A2—this profile is called depression).
The sand-loess deposits opened in quarries near the villages Krasnoe (first terrace of Desna) and Telec (second terrace) formed in the second and first half of the Valdai (Wurm) period, respectively [2]. Loess deposits of quarries cover the sandy sediments with numerous signs of permafrost, such as disturbance by cryoturbation processes (Figure 2d), gleying and ferruginous horizons. Location 1 – Telec quarry stratigraphy contains modern soil of micro-elevation (0–120 cm). Modern soil has formed on loess-like sediment (120–250 cm, C1-3). The paleosol of the Lascaux interstadial is fixed at depths of 250–300 cm (Bb-BCb) and represented by light brown sandy loam sediment with a cemented ferruginous sand horizon ORTZ1 (350−420 cm). The underlying stratum is composed of sand with traces of gleying. Location 2—Krasnoe quarry stratigraphy contains modern soil of micro-depression (0–220 cm) with dark brown Holocene paleosol or second humic horizon (Ab 50–85 cm, Figure 2c). The underlying loess-like deposits (220–470 cm, C1-2) contain iron-manganese spots along the pores, clay cutans. Cryoturbated soil of Bølling-Allerød is fixed at depths 470–495 cm (Bb) and 495–500 cm (BCb). Paleosol is represented by reddish-brown loam with ferruginous spots. The underlying sand stratum (500–570 cm) also contains waterlogging traces - bluish, reddish colors and ferruginous horizons. Location 3—is a modern soil (0–110 cm) with second humic horizon (Ab, 40–65 cm) (Table A1).
Thus, these loess-paleosol sequences reflect the transition from Late Pleistocene to Holocene warming for Desna river landscapes with warmer periods and permafrost melting episodes. Sand deposits with traces of gleying alternate with two Late Pleistocene paleosols and are covered with loess-like loam on which Holocene paleosols and modern soils are formed. The paleosol of the Krasnoe loess-soil series was found in cryoturbated sand deposits, while the Telec quarry soil divides the sand deposits from the upper loess-like sediments and has flat borders.
A radiocarbon analysis of extractable humic acids was carried out by the method of liquid scintillation counting at the Kyiv Radiocarbon Laboratory (Institute of Environment Geochemistry, Ukraine) [51]. The content of the 14C isotope was measured on a Quantulys 1220 T spectrometer. Data calibration was done using OxCal v4.2.4 program [52] with IntCal13 curve [53]. Humic acids were chosen as a sample for dating due to the absence of other organic residues (such as bones, coal) which are more common for the cultural layers of archeological sites.
The qualitative and quantitative determination of n-alkanes was carried out by capillary gas–liquid chromatography. The extraction carried out with chloroform using an automatic extractor ASE 200 at a temperature of 100 °C. Separation of the nonpolar fraction of hydrocarbons carried out on aluminium oxide Al2O3 (Brokman activity level-II). The analysis was carried out on an Agilent 6890 gas chromatograph with a flame ionization detector and a column DB-1 ms (length—30 m, diameter—0.25 mm, phase thickness—0.25 μm). A standard mixture of n-alkanes C12-C36 was used for calibration with individual alkanes.
n-Alkanes (normal alkanes)—unbranched saturated aliphatic hydrocarbons are biomarkers of such plant groups as trees, mosses, grasses, which have a different ratio of these hydrocarbons. It is known that nC27-nC29n-alkanes dominate in most modern trees and shrubs, and nC31-nC33n-alkanes—in grasses [18] and are resistant to biodegradation. Data are presented in μg/kg of dry weight.
To assess the predominant source of n-alkanes and the characteristics of the total spectrum and to estimate the degradation OEP index (odd-over-even predominance) is used: OEP = (nC25 + nC27 + nC29+ nC31 + nC33)/(nC24 + nC26 + nC28 + nC30 + nC32) [13]. We also used informative indices such as ACL27-33 (average chain length), CPI27-33 (carbon preference index), and Paq (contribution of aquatic plants).
To determine the carbon isotopic composition of soil carbonates samples were kept in a muffle stove at 500 °C for 1 hour to remove organic matter. The 13C/12C (δ13C) ratio was measured on a mass spectrometer Thermo-Finnigan Delta V Plus IRMS and an elemental analyzer Thermo Flash 1112. Standart-PDB. The carbon isotope ratio is a well known marker for searching of C3 or C4 vegetation transitions.

3. Results

As is evidenced from the Figure 3 and Figure 4 that show distribution of magnetic susceptibility values (χ), mineral phosphorus content, organic carbon isotope composition of Telec quarry sequence (Figure 3) and Krasnoe quarry sequence (Figure 4) based on previous [13,14,15,16] and new data, buried soils are well distinguished by these paleoindicators as well as by the organic carbon and phosphorus content (Appendix A, Table A1).
According to dating results, the second humus horizon of the micro-depression soil corresponds to the Holocene Subatlantic period. The soil of the micro-elevation has no second humic horizon (the common feature of the investigated landscapes), but it has a thin Atlantic horizon at a depth of 85–99 cm with age 6690 ± 110 (Table 1).
More ancient paleosol of the Last Glacial period in the Krasnoe outcrop (Figure 4) under the micro-depression profile has data 12930 ± 170 years BP and marks the Bølling-Allerød warm period. The sequence of Telec outcrop under the micro-elevation soil contains Lasko (Lascaux) interstadial soil (i.e., the Trubchevsk horizon—in Russian stratigraphic scales) 16,500 ± 230 BP (Table 1). These two Late Pleistocene soils correspond to MIS2 according to [54,55]).
n-Alkanes measurement was carried out in the range of chain length 17−34. The maximum concentration of n-alkanes was recorded for the Holocene paleosol—the second humus horizon of modern soil in depression (2668.6 μg/kg or 2.67 μg/g dry weight) (Table A2). An analysis of n-alkanes distribution allows us to conclude that the organic matter of the second humus horizon in the depression is better preserved than in the plowed upper part of the profile of micro-depression. We also fixed the strong predominance of mid-chain n-alkanes in horizons under modern humic horizon (AE, EB) (Figure 5 and Figure 6). Therefore, we will further use data on the second humus horizon from the depression profile (Ab, 40−65cm, Figure 7), where this horizon has a predominance of C27 and C29 alkanes.
The maximum concentration of alkane C31 (coming mainly from grassy vegetation) was measured for the Late Pleistocene interstadial paleosols of the Krasnoe and Telec quarries (Table A2). The index C31/C29 for these soils are 1.64 and 1.15, respectively, while in the Holocene samples it is less than 1. Paleosols are characterized by a predominance of odd alkanes which indicates the origin from vascular plants (OEP = 4−6).
Average chain length (ACL) shows the transition from 31 and 30 for the Late Pleistocene soils to 29, 27—for the Holocene soils. Furthermore, the maximum value of index (nC31 + nC33) / (nC27 + nC29) was fixed for Late Pleistocene soils. We also calculated an index which characterized the contribution of aquatic plants (Pq) [44]. It was a fixed, low contribution of these plants in the Late Pleistocene, and slightly larger influence in the Holocene soils—with the exception of AE horizons with possibly degraded organic matter and high mid-chain alkane concentrations (Table A2, Figure 5).
The loess covered Lasko interstadial soil has a maximum value of δ¹³Ccarb. (−8.3‰) as well as heaviest organic carbon isotope composition (−23.1‰) reflected most arid episode after Lasko warming (Table A1). However, the paleosol of the Lasko warm period has a very light weight isotope composition of pedogenic carbonates. Such isotope values require further investigation, However, few similar data are known on pedogenic carbonates recorded in sediments and paleosols of the Late Pleistocene-Early Holocene [56,57].

4. Discussion

By analyzing current and previously obtained data, we can conclude that the Bølling-Allerød warm period was characterized by a drier and warmer climate than the Lasko interstadial (i.e., the Trubchevsk interstadial—regional name). Despite the cryogenic disturbance, the paleosol of Bølling-Allerød has the features of soil formed in more favorable and warm conditions: higher values of organic phosphorous (106 mg/kg, Table A1), magnetic susceptibility (Figure 4), total amount of n-alkanes. Stable carbon isotopic composition reflects (δ13Corg = −24.8‰; δ13Ccarb.= −8.8‰) an increase of arid conditions in comparison with the overlying and underlying deposits and Lasko paleosol (Table A1). Furthermore, it has the largest proportion biomarkers ((nC31 + nC33) / (nC27 + nC29) = 1.95, ACL = 31) in comparison to other recorded paleosols (Table A2) which indicates the dominance of herbaceous plant communities. Thus, the landscapes were productive and allowed for soil formation. The well-spatially-expressed and undisturbed soil of the Lasko interstadial had apparently crowned the permafrost level; therefore, it has flat boundaries. Its formation took place in a more hydromorphic environment and was accompanied by processes of carbonates and iron accumulation influenced abnormally light carbonate isotope composition (Table A1). Nevertheless, the C31/C29 index in Lasko soil (1.15) is near 1 and shows the very slight predomination of grassy vegetation biomarkers. On the other hand, some authors have documented the accumulation of alkane C29 in sedges [40].
Further early palynological investigations of the Russian Plain [1] correlate with our conclusion about the warmer and drier period of Bølling-Allerød in comparison with Lasko interstadial. In the Middle Dnestr valley (Ukraine), the author detected three interstadial warmings—Lasko, Bølling, Allerød, and registered the transition of vegetation from mixed forests of pine, oak, hornbeam, ash, linden, elm, etc., through to the domination of forbs-serial meadows in Bølling to complex vegetation with broad-leaved forests along river valleys and ravines in Allerød. For the Lasko period in the middle Desna valley, the author also highlights the predominance of woody vegetation (pine, cedar-pine, birch-pine forests with undergrowth from birch, alder, juniper, willow) and indicates the periglacial nature of the landscape (ephedra, Artemisia) [1]. Our research also suggests the coexistence of woody and herbaceous vegetation during these interstadials, which is reflected in a noticeable proportion of C29 alkane (nC31/nC29 = 1.64—for Bølling-Allerød and 1.15—for Lasko soil) and not heavy values of the carbon isotope ratio (from −26‰ to −24‰) indicated the predominance of vegetation with C3-type of photosynthesis. However, at the same time, the predominance of grasslands was reflected. Based on the distribution of n-alkanes and the index ACL, the Bølling-Allerød soil was formed under conditions of a larger proportion of grasses compared with the soil of the Lasko interstadial and modern soils.
Based on the available palynology data [58,59], periglacial vegetation was characteristic of both studied Late Pleistocene periods in Eastern Europe and in particular the Russian Plain. The period of the last transition of the glacier (LGT, 17−12.4 kyr BP) is characterized by the predominance of tundra and forest-tundra species to the north of 48°−49° N, sometimes passing south to the latitudes of Bryansk (52° N) along the valleys of large rivers. Steppe and meadow-steppe species prevailed south of 47−51° N. Thus, the studied territories are located in the boundary position between the tundra/forest-tundra and the steppe zones, and the authors [58] relate it to the periglacial forest-steppe zone. At the same time, the vegetation of the Lasco interstadial was not investigated. According to palynological data [59], the Bølling-Allerød period was characterized by a wetter and warmer climate. Nevertheless, despite a slight shift in natural zonality revealed by palynologists [59], during this warm period, the vegetation of the studied Bryansk region is referred to the periglacial forest-steppe zone, as well as at earlier stages of Late Glacial.. Pine-birch forests dominated in combination with meadow steppes and tundra associations. Thus, the proportion of open grassy landscapes can be determined using isotopic ratios and analyses of the distribution of n-alkanes, which allow us to clarify the differences between objects with similar palynological characteristics.
The clearly visible dominance of woody biomarkers in Holocene soils—including modern humic horizons ((nC31 + nC33)/(nC27 + nC29) = 0.23-0.63, ACL=27-29, Table A2)—correlate with a light isotopic composition (Table A1, Figure 5, Figure 6 and Figure 7). A similar distribution of n-alkanes is characteristic of woody biocenoses, which mainly carry out the C3 type of photosynthesis. The Subatlantic paleosol of the second humus horizons is characterized by a more humid and warm climate compared with the modern climate (this paleosol distinguished by a high amount of organic carbon and phosphorus, Table A1, Location 2).
The results of n-alkanes composition are more reliably a record of change in vegetation at the Late Pleistocene-Holocene transition, confirming the hypothesis of the dominance of biocenoses with a higher proportion of grassy landscapes. The predominance of mid-chain alkanes in AE, EB horizons of modern arable soils is probably a result of degradation associated with microbiological activity [10].
The data presented in this article do not yet characterize the numerous climatic oscillations in the transition from the Late Glacial to the Holocene, and were carried out as the first study in this direction of biomarkers investigations for the Russian Plain in order to catch changes in vegetation. Thus, our research will continue to clarify the data in the future.

Author Contributions

Conceptualization, N.K., E.S.; methodology, N.K.; investigation, E.S., N.K., I.K.; writing—original draft preparation, E.S.; N.K.; writing—review and editing, E.S., N.K., I.K..; supervision, N.K.; project administration, N.K., I.K., E.S; funding acquisition, N.K. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by grant number 17-14-01120 of Russian Science Foundation.

Acknowledgments

The authors are thankful to Demin V.V., Streletskiy R.A. for the help in n-alkanes measurements.

Conflicts of Interest

The authors declare no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results”.

Appendix A

Table
Table A1. Characteristics of organic matter *.
Table A1. Characteristics of organic matter *.
LocationAge, Years BPHorizon, Depth, cmCorg.,
% *		P2O5 org,
mg/kg *		δ13Corg, ‰ *δ13Ccarb, ‰ *n-alkane, tot., μg/g d.w. **
1. Quarry,
v. Telec,
micro-
elevation		 Ap, 0−301.2115.0−26.1non-carb.1.03
AE, 30−350.417.8−25.4non-carb.0.19
EB, 35−460.218.4−24.7non-carb.0.41
BC, 46−650.210.6−24.7non-carb.-
C, 65−850.20.0−24.1non-carb.-
6690 ± 110Ab, 85−990.497.2−25.4−13.5-
C1, 99−1200.383.9−25.3−10.0-
C2, 120−..0.238.9−25.7−8.3-
C3, 100−2500.529.9−23.1non-carb.
16,500 ± 230Bb, 250−2750.30.0−26.5−22.30.00
BCb, 275−3000.468.0−25.6−22.40.23
ORTZ1, 350−4200.344.5−26.5−22.0-
Eg, 770−9700.10.0−26.6non-carb.-
C4, 970−10000.10.0−26.7non-carb.-
C5, 1000−13000.20.0−25.7non-carb.-
2. Quarry,
v.Krasnoe,
micro-
depression		 Ap, 0−301.8178.7−25.0non-carb.0.73
AE, 30−501.5311.9−26.4non-carb.0.10
2180 ± 60, 1650 ± 60*** Ab, 50−852.3635.8−28.4non-carb.0.15
AEb, 85−1001.3389.8−26.2non-carb.-
Eb, 100−1250.4125.4−25.6non-carb.-
EBb, 124−1400.60.0−26.1non-carb.-
Bb, 140−1750.30.0−26.1non-carb.1.02
C1, 175−2700.20.0−25.3non-carb.-
C2,fe,1, 445–4700.20.0−26.6non-carb.-
12,930 ± 170Bb2, 470–4950.4106.3−24.8−8.80.80
BCfe,b2, 495−5000.10.0−25.3non-carb.-
Eg, 500−5100.10.0−27.0non-carb.-
BCfe,b3 510−5200.17.8−27.2non-carb.-
C3 520−5700.12.6−26.7non-carb.-
3. Modern soil, depression * A, 10−453.4271.2−32.7non-carb.1.14
*** Ab, 40−654.0170.0−29.5non-carb.2.67
AEg, 60−800.850.8−27.5non-carb.2.15
Eg, 80−1100.30.0−27.0non-carb.-
* published data [13], ** unpublished data, *** second humic horizons of modern soils.
Table
Table A2. n-Alkane parameters *.
Table A2. n-Alkane parameters *.
Sample, Depth, cmRelief PositionAge, Years cal. BPn-alkane tot.(C17-36),
μg/kg d.w.		CmaxOEP1ACL27-33CPI27-33(nC31 + nC33)/
(nC27 + nC29)		Paq
1. Quarry Telec
Ap, 0−30micro-elevation 1027.9C294.3293.50.630.30
AE, 30−35 190.2C21-27-01.0
EB, 35−46 406.2C200.7271.400.93
BCb,
275−300		16,500 ± 230230.5C313.8302.61.390.11
2. Quarry Krasnoe
Ap, 0−30micro-depression 730.0C294.3293.50.400.44
AE, 30−50 97.6C22 1.00
Ab, 50−852180 ± 60, 1650 ± 60151.3C21-27-01.00
Bb,
140−175		 1020.3C210.8281.40.080.81
Bb2,
470−495		12,930 ± 170804.3C315.7314.01.950.10
3. Modern soil, depression
A, 10−45depression 1142.6C293.4293.70.230.51
Ab, 40−65 2668.6C294.8294.80.270.46
AEg, 60−80 2153.9C250.9281.00.140.71
1 OEP = (nC27 + nC29 + nC31 + nC33)/(nC26 + nC28 + nC30 + nC32); CPI27-33 = 0.5*(nC27 + nC29 + nC31 + nC33)/(nC28 + nC30 + nC32 + nC34); ACL27-33 = (27nC27 + 29nC29 + 31nC31 + 33nC33)/(nC27 + nC29 + nC31 + nC33); Paq = (nC23 + nC25)/(nC23 + nC25 + nC29 + nC31). *–unpablished data

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Figure 1. Location of studied sites, internet source; https://www.nationsonline.org/oneworld/map/European-Russia-map.htm.
Figure 1. Location of studied sites, internet source; https://www.nationsonline.org/oneworld/map/European-Russia-map.htm.
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Figure 2. (a) Micro-depression in upper part of quarry; (b) micro-depression in landscape; (c) second humus horizon, micro-depression profile; (d) Cryoturbation within sandy deposits, Krasnoe outcrop.
Figure 2. (a) Micro-depression in upper part of quarry; (b) micro-depression in landscape; (c) second humus horizon, micro-depression profile; (d) Cryoturbation within sandy deposits, Krasnoe outcrop.
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Figure 3. Loess-paleosol sequence with micro-elevation (on the top), Telec quarry, magnetic susceptibility, inorganic phosphorus, stable carbon isotope curves, average chain length in n-alkane distribution.
Figure 3. Loess-paleosol sequence with micro-elevation (on the top), Telec quarry, magnetic susceptibility, inorganic phosphorus, stable carbon isotope curves, average chain length in n-alkane distribution.
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Figure 4. Loess-paleosol sequence with micro-depression (on the top), Krasnoe quarry, magnetic susceptibility, inorganic phosphorus, stable carbon isotope curves, average chain length in n-alkane distribution.
Figure 4. Loess-paleosol sequence with micro-depression (on the top), Krasnoe quarry, magnetic susceptibility, inorganic phosphorus, stable carbon isotope curves, average chain length in n-alkane distribution.
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Figure 5. n-alkane distribution in soil of micro-elevation and interstadial soil from loess-paleosol sequence under it.
Figure 5. n-alkane distribution in soil of micro-elevation and interstadial soil from loess-paleosol sequence under it.
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Figure 6. n-Alkane distribution in soil with second humus horizon (Ab) of micro-depression and interstadial soil from loess-paleosol sequence under it.
Figure 6. n-Alkane distribution in soil with second humus horizon (Ab) of micro-depression and interstadial soil from loess-paleosol sequence under it.
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Figure 7. n-Alkane distribution in native soil with second humus horizon (Ab), depression.
Figure 7. n-Alkane distribution in native soil with second humus horizon (Ab), depression.
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Table
Table 1. Radiocarbon data for paleosols of Bryansk region.
Table 1. Radiocarbon data for paleosols of Bryansk region.
SampleDepth (cm)Lab. NumberMaterialRadiocarbon Age (yr)Calendar Age (yr)
Ab, micro-depression50−85Ki-18775Humic acids1650 ± 601σ 1 334−530 BC
2σ 257−539 BC
Ab, micro-depression50−85Ki-17415Humic acids2180 ± 601σ 360−270 BC
2σ 390−90 BC
Ab, micro-elevation85−99Ki-18776Carbonates6690 ± 1101σ 5706−5527 BC
2 5837−5392 BC
Bb2, Krasnoe470−495Ki-17413Humic acids12930 ± 1701σ 14000−13200 BC
2σ 14200−12400 BC
Bb, Telec250−275Ki-17414Humic acids 16500 ± 2301σ 18150−17300 BC
2σ 18600−16900 BC
1 1σ—probability 68.2%; 2σ—probability 95.4%.

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Stolpnikova, E.; Kovaleva, N.; Kovalev, I. n-Alkane Distribution—A Paleovegetation Change Indicator during the Period from Late Glacial to Late Holocene on Russian Plain (Bryansk Region). Geosciences 2020, 10, 86. https://doi.org/10.3390/geosciences10030086

AMA Style

Stolpnikova E, Kovaleva N, Kovalev I. n-Alkane Distribution—A Paleovegetation Change Indicator during the Period from Late Glacial to Late Holocene on Russian Plain (Bryansk Region). Geosciences. 2020; 10(3):86. https://doi.org/10.3390/geosciences10030086

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Stolpnikova, Ekaterina, Natalia Kovaleva, and Ivan Kovalev. 2020. "n-Alkane Distribution—A Paleovegetation Change Indicator during the Period from Late Glacial to Late Holocene on Russian Plain (Bryansk Region)" Geosciences 10, no. 3: 86. https://doi.org/10.3390/geosciences10030086

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