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Article

Effects of Climate Change and Fire on the Middle and Late Holocene Forest History in Yenisei Siberia

1
Department of Quaternary Paleogeography, Institute of Geography of the Russian Academy of Sciences, Staromonetny lane, 29, Moscow 119017, Russia
2
Department of Physical Geography and Landscape Science, Faculty of Geography, Lomonosov Moscow State University, GSP−1, Leninskie Gory, 1, Moscow 119991, Russia
3
Department of Geography, Ecology and General Biology, Orel State University Named After I.S. Turgenev, Komsomol’skaya Str., 95, Orel 302026, Russia
4
Context Anthropology Laboratory, Institute of Archaeology of the Russian Academy of Sciences, Dmitriya Ulyanova St., 19, Moscow 117292, Russia
5
Department of Cartography and Geoinformatics, Faculty of Geography, Lomonosov Moscow State University, GSP−1, Leninskie Gory, 1, Moscow 119991, Russia
6
Laboratory of Biogeochemical Cycles in Forest Ecosystems, V.N. Sukachev Institute of Forest SB RAS, Federal Research Center “Krasnoyarsk Science Center SB RAS”, Akademgorodok 50/28, Krasnoyarsk 660036, Russia
7
School of Ecology and Geography, Siberian Federal University, Svobodny av., 79, Krasnoyarsk 660041, Russia
8
Department of Meteorology and Climatology, Faculty of Geography, Lomonosov Moscow State University, GSP−1, Leninskie Gory, 1, Moscow 119991, Russia
*
Author to whom correspondence should be addressed.
Forests 2023, 14(12), 2321; https://doi.org/10.3390/f14122321
Submission received: 5 October 2023 / Revised: 19 November 2023 / Accepted: 24 November 2023 / Published: 26 November 2023

Abstract

:
This study presents the long-term forest history in the forest–tundra ecotone of the Low Yenisei River basin. The new high-resolution pollen and macroscopic charcoal data were inferred from the 8.6 m long peat archive covering the last 6300 years. Climate reconstructions are based on the application of the best modern analogue technique using pollen data. Our findings suggest an alternation of phases of middle-taiga forests of Larix sibirica, Abies sibirica, Picea obovata, and Pinus sibirica (intervals of climate warming: 6320–6050, 5790–5370, 4480–4220, and 3600–2700 cal yr BP, respectively) and open larch woodlands with the participation of Betula, Picea, and Pinus sibirica, typical for northern taiga (intervals of climate cooling and increasing humidification: 5370–4480, 4220–3600 cal yr BP, respectively). The vegetation pattern of the region became similar to the modern one around 2700 cal yr BP. Climate warming caused a northward shift of vegetation-zone boundaries in Yenisei Siberia and an expansion of the range of Abies sibirica by about 200 km to the north compared to the present day. The increased frequency of fires and biomass burning during warm periods may promote the melting of the local permafrost, thereby enhancing the tree growth and regeneration.

1. Introduction

Current climate conditions are characterized by a steadily rising global temperature, changing precipitation patterns, and growing frequency and severity of extreme weather events [1]. High-latitude forest ecosystems have become highly vulnerable to environmental change in recent decades, as climate warming has been more pronounced in the high-latitude regions than in other parts of the world [2]. Rising air temperatures and more frequent heat waves with reduced precipitation are expected to increase drought conditions and the risk of wildfires in the region [3,4]. These changes may also lead to permafrost degradation and shifts in vegetation patterns of tundra and forest biomes [5,6,7,8,9].
The palaeoecological reconstruction of the history of forests and fires in the past is crucial for a better understanding of the possible consequences of the current climate change for the forest ecosystems. Available Holocene paleoenvironmental reconstructions from various natural archives in the Arctic show a remarkable ecosystem response to past climate variability [10,11,12,13,14,15,16,17]. Especially for the area of northern Siberia, high regional variability in long-term vegetation and climate dynamics was revealed, with several phases of climate fluctuations. Paleoenvironmental reconstructions based on multiproxy records from the inner part of Siberia [18,19,20,21,22,23] showed a high sensitivity of forest ecosystems in Eastern and Western Siberia to Holocene climate changes. A close relationship between positive temperature anomalies and wildfire frequency was also shown [24,25,26,27,28,29,30]. However, despite their substantial contribution to our understanding of natural processes in the high-latitude regions, high-resolution palaeoecological records in northern Siberia are still very limited. Therefore, new studies are very important in this case to obtain more detailed information on possible mechanisms of climate–vegetation interaction in past epochs in the study region, thereby confirming or disproving previously formulated hypotheses.
Our present study of forest and fire history focuses on the forest area near the town of Igarka in Russia, located on the eastern margin of the West Siberian Lowlands in the Lower Yenisei River Basin. The plant cover of the various types of mires and the peat stratigraphy in the study area have been described by Katz [31] and Vasilchuk et al. [32]. The previous palynological and plant macrofossil records from this region were obtained by Piavchenko [33], Levkovskaya et al. [34], and Andreev and Klimanov [12].
In our paper, we introduce the novel high-resolution pollen and macroscopic charcoal data obtained from an 8 m long peat sequence covering the mid- to late-Holocene. The objectives of the study are: (1) to reconstruct the forest and fire history; (2) to reveal the relationships between vegetation change, wildfire frequency, and climate in the study area; and (3) to correlate our new findings with the Holocene climate change and environmental dynamics in the Russian Arctic.

2. Material and Methods

2.1. Study Area

The study area is located near the town of Igarka (Figure 1) in the Turukhansk district of the Krasnoyarsk region (Russia). The topography in this area is mostly flat to gently sloping, with low elevations ranging from 30 to 50 m above sea level. Abundant peatlands with perennial frost mounds are widespread.
The climate of the study area is subarctic, with prolonged and severe winters and short but relatively mild summers [35]. The mean annual air temperature is about −8.5 °C, and the mean temperatures of the coldest (January) and warmest (July) months are −28.9 °C and 15.6 °C, respectively [36]. Precipitation reaches 486 mm per year. The region belongs to the continuous permafrost area [37].
The study area belongs to the northern-taiga vegetation zone. The main forest forming trees are Larix sibirica Ledeb., Picea obovata Ledeb., Betula pendula Roth., and Pinus sibirica Du Tour. Our field observations showed the predominance of open larch, spruce-larch and pine-larch woodlands with a canopy density of 0.4–0.5 and extensive areas of early successional stands after clear-cutting and fires.
As a paleoarchive for the study of the Holocene forest and fire dynamics, we chose the peatland (hereafter Igarka peatland, 67°31′53.77″ N, 86°38′05.65″ E) situated about 10 km northeast of the town of Igarka (Figure 1 and Figure 2). A detailed description of the peatland vegetation, the results of preliminary charcoal and plant macrofossil analysis and loss on ignition (LOI) measurements of the Igarka peat core, as well as the pollen and plant macrofossil records from the short peat core extracted from an unfrozen hollow near the study site have been published previously by Novenko et al. [38,39] and are used to discuss the palynological and macroscopic charcoal records presented here for the first time.
Figure 1. Location of the study area on the map of North Central Siberia. 1—location of the study area, 2—location of the sampling site, 3–6—boundaries of modern geographical ranges of tree species [40]: 3—Pinus sylvestris, 4—Abies sibirica, 5—Pinus sibirica, 6—Picea obovata.
Figure 1. Location of the study area on the map of North Central Siberia. 1—location of the study area, 2—location of the sampling site, 3–6—boundaries of modern geographical ranges of tree species [40]: 3—Pinus sylvestris, 4—Abies sibirica, 5—Pinus sibirica, 6—Picea obovata.
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The Igarka peatland covers an area of 12.4 ha and consists of ridges of perennial frost mounds (palsas) up to 5 m high and over 100 m wide, separated by thawed hollows (200–300 m). The plant cover of the palsa consists of lichens (70%) and feathermosses (20%) with Betula nana L. and Ledum palustre L. The vegetation of the hollows is formed by various species of Carex, feathermosses and Betula nana thickets [38].

2.2. Sediment Sampling and Radiocrbon Dating

The 860 cm long sediment core recovered from the perennial frost mound (4.5 m high and about 100 m wide) was used to obtain the high-resolution pollen and macrocharcoal records. A portable drilling station equipped with a motorized piston corer was used to collect the core in late August 2020.
The sediment core comprised peat deposits (845 cm) with numerous ice lenses and a layer of unstratified dark gray clay with plant detritus (15 cm). The lower part of the peat sequences (845–516 cm) is formed by highly humified minerotrophic peat composed of the remains of feathermosses such as Hamatocaulis vernicosus (Mitt.) Hedenäss, Drepanocladus aduncus (Hedw.) Warnst., and Scorpidium scorpioides (Hedw.) Limpr. [38]. Alternation low-decomposed peat horizons with dominance of Sphagnum mosses (Sphagnum girgensohnii Russow, S. teres (Schimp.) Ångstr., and Sphagnum squarrosum Crome) and highly decomposed peat with remains of feathermosses, herbs, and Carex occur between 516 and 220 cm. Carex species (C. chordorrhiza Ehrh., C. lasiocarpa Ehrh., and C. aquatilis Wahlenb.) predominate among the peat-forming plants, which alternate with the layers of brown and feathermosses in the depth interval 220–51 cm and are replaced by peat with Eriophorum vaginatum L., Scheuchzeria palustris L., and abundant Sphagnum stems between 51 and 17 cm. The uppermost layer of the peat sequence is represented by remains of Ledum palustre, Cladonia, Cetraria, and Polytrichum strictum Brid.
Pollen was sampled at 5 cm intervals. Macrocharcoal samples were collected continuously, with sampling intervals varying from 0.5 to 5.0 cm (average 2.8 cm) depending on the amount of ice and peat material in the samples. In total, 136 pollen samples and 537 macro-charcoal samples were analyzed.
The radiocarbon dating was performed for 20 bulk peat samples (Table 1). The samples were first prepared at the Center of Common Use “Laboratory of Radiocarbon Dating and Electronic Microscopy” of the Institute of Geography of the Russian Academy of Sciences (Moscow), and then dated by accelerator mass spectrometry at the Center for Applied Isotope Studies of the University of Georgia (USA). The “Bacon” package [41] in the R language environment [42] was used to calculate the age–depth model (Figure 3). Calibration of 14C dates was performed with the “Bacon” package using the Intcal 20 calibration curve [43].

2.3. Pollen Analysis

Peat samples for pollen analysis (1 cm3) were prepared according to Moore et al. [44]. The samples were heated in 10% KOH for 10 min to remove humic material. The residue was then sieved through a 200 μm mesh, followed by HF treatment [45]. The residue was then finely sieved through 10 μm mesh with 10% Na4P2O7 in an ultrasonic bath for less than one minute. The sample preparation was completed by acetolysis in a water bath for 5 min, using propionic anhydride [46] to dissolve the cellulose. Lycopodium spores were added prior to chemical treatment to determine pollen and charcoal concentrations [47]. Pollen identification was performed using a Zeiss Axio Lab A1 microscope at 400× magnification according to Reille [48] and Beug [49]. Identification of non-pollen palynomorphs (NPPs) is based on van Geel [50], Shumilovskikh et al. [51], and the NPP Image Database [52]. The calculation of pollen percentages was based on the total terrestrial pollen sum, i.e., arboreal pollen (AP) plus non-arboreal pollen (NAP), excluding aquatic plants, spores, and NPPs. At a minimum, 350–400 pollen grains were counted per sample (AP + NAP). Microscopic charcoal (<100 µm) concentrations were assessed using Clark’s point-count method [53]. Pollen and plant macrofossil diagrams were created using the programs Tilia and TGView [54].
During the extraction of the peat core in the field, four large wood fragments (up to 5 cm in length) were found and identified according to Benkova and Schweingruber [55].

2.4. Charcoal Analysis

Macroscopic charcoal analysis was used to determine the frequency of forest fires. Samples of fresh peat with volume of 1 cm3 were stored in bleach (100 mL of 10% NaOCl) at room temperature for 24 h [56]. Then, the samples were gently sieved through a 125 μm mesh and the residue was carefully placed on labelled Petri dishes and charcoal particles were registered using the MOTIC SMZ-171 stereoscopic microscope at 40× magnification. Data processing for charcoal analysis was performed in the “Tapas” package version v.0.1.0 [57] in the R language environment [42]. In our study, we used the following parameters: charcoal concentration (pieces cm−3), charcoal accumulation rate (pieces cm−2 yr−1, CHAR), CHAR of the interpolated record (Cint), and the low-frequency trend in CHAR (Cback). We used a 10-year period to interpolate the record, which allows accurate documentation of peaks at relatively high peat accumulation rates. The peaks of the charcoal accumulation were determined as a relationship: Cpeak = Cint − Cback [57]. We assume that the peaks of the charcoal accumulation rate indicate the local fire episodes (one or several successive fires). These peaks were separated from the background charcoal (Cback) using the method of smoothing time-series data using moving medians. A 300-year window was used to smooth the data set for Cback estimation. The corresponding threshold value within the Cpeak component was set at the 95th percentile of the Gaussian mixture model.

2.5. Climate Reconstruction

The best modern analogue (BMA) technique was used to reconstruct the mean July temperature and annual precipitation. Details of the BMA approach are presented in many publications devoted to paleoclimate research [58,59,60,61,62] and references therein. Using the BMA technique, we compare the fossil pollen assemblage with modern pollen assemblages. We use squared-chord distances (SCD) [58] as an index of dissimilarity. In the present study, we consider two spectra to be analogous if their SCDs were less than the threshold equal to 2. The reconstructed values of temperature and precipitation were calculated as weighted averages of 8 modern analogues. The BMA calculations were performed in the “analogue” package [63] in the R language environment [42] (see Supplementary Material S1).
The training set of the modern pollen assemblages in our study includes 173 pollen spectra from different landscapes in the northern Siberia and Yakutia. A total of 142 sites were derived from the Eurasian Modern Pollen Database-2 [64], and 30 pollen assemblages are our own surface samples collected in the period 2020–2022 in the area of Igarka and several regions of Central Siberia. Climatic information was obtained from the reference book “Climate of Russia” [36].
Leave-one-out cross-validation [65] showed a relatively good correlation of the pollen-based July temperature and annual precipitation reconstructions with modern climate characteristics. We obtained R-squared (R2 = 0.89, p < 0.05), root mean squared error (RMSE = 1.2 °C), and mean absolute error (MAE = 0.77 °C) for the mean July temperature and R2 = 0.79, RMSE = 51 mm, and MAE = 32 mm for the mean annual precipitation, which is basically sufficient for reconstructing climate changes during the Holocene.

3. Results

3.1. Chronology

According to the data obtained, the accumulation of the sediment core began at 6320 cal yr BP. With a sampling interval of 50 cm, the radiocarbon dates show a progressive increase in age downwards (Figure 3, Table 1), except for a few inversions. The 14C dates at the depths of 252 cm (14C 4080 ± 20 yr BP) and 449 cm (14C 4340 ± 20 yr BP) revealed the ages lying within the uncertainty of the model of the linear peat growth (Figure 3). A sample from the depth of 650 cm (14C 4315 ± 25 yr BP) indicated a much younger age as compared to the over- and under-lying samples, probably due to the bioturbation or sampling error.
The age of most of the peat core corresponds to the time interval between 5500 ± 20 14C yr BP (6320 ± 20 cal yr BP) and 3230 ± 20 14C yr BP (3440 ± 20 cal yr BP), as indicated by radiocarbon dates derived from depths of 860 cm and 50 cm, respectively. Thus, the average temporal resolution of the peat core, except for the uppermost 50 cm, varies from 0.25 to 7 yr cm−1. This rate of peat accumulation is extraordinarily high compared to the average peat growth in Western Siberia [66,67] and could be overestimated due to peat expansion by ground ice lenses in the perennial frost mound. We observed several ice layers up to 5 cm thick in the studied peat core, as well as numerous inclusions of ice crystals in the peat. Nevertheless, the specificity of peat growth in the period 6320–3440 cal yr BP gives us the opportunity to perform the paleoenvironmental reconstruction with decadal resolution.
The peat accumulation rate decreased significantly between 3440 and 1850 cal yr BP, as indicated by the radiocarbon date of 1930 ± 20 14C yr BP (1850 ± 40 cal yr BP) found at a depth of 15 cm. The average temporal resolution of this peat layer is about 42 yr cm−1. The chronology of the uppermost 15 cm of the peat core above the 14C date 1930 ± 20 yr BP is unclear. We suggest that the peat accumulation rate may be underestimated because of peat disturbances in the result of water erosion of the palsa surface and wildfires. During the field observations, we recorded patches of bare peat and cracks on the palsa surface and slopes and found charcoal fragments and charred wood at the depths of 10–11 and 13–14 cm. The damage of the uppermost peat layers in perennial frost mounds and peat plateaus is common for peatlands in the Arctic region [32,67].

3.2. Pollen Analysis and Vegetation History

The results of pollen analysis showed that the vegetation dynamics over the past 6320 years was an alternation of phases of middle-taiga forests of Larix, Pinus sibirica, Picea, and Abies (intervals 6320–6050, 5790–5370, 4480–4220, and 3600–2700 cal yr BP, respectively) and open Larix woodlands with the participation of Picea, Pinus sibirica, and Betula, typical for northern-taiga (intervals 5370–4480, 4220–3600 cal yr BP and 2760 cal yr BP–present, respectively). Eight pollen assemblage zones (PAZ) were identified in the pollen diagram of the studied peat core (Figure 4).
PAZ 1 (865–750 cm, 6320–6050 cal yr BP). Arboreal pollen predominated in the assemblages (90%–98%), mainly due to the high pollen values of Pinus, Betula alba-type (40%–70%), and shrubs (Betula nana, Alnus fruticosa Rupr.). The proportion of Picea and Abies pollen did not exceed 10%–20%. Pollen of Juniperus and Salix occurred in small quantities. Non-arboreal pollen was represented by Poaceae, Cyperaceae, Artemisia, and Rosaceae (0.5%–2%). With slight variations in abundance, these taxa were consistently recorded throughout the peat sequence. Pollen of Onagaraceae occurred sporadically. The group of spores was abundant and diverse. Spores of Lycopodium annotinum L. (up to 40%), L. clavatum L., L. pungens (Desv.) Bach. Pyl. ex Iljin, and Polypodiaceae (up to 10%) were recorded; values of Equesetum reached 70%–100% compared to the sum of AP + NAP. Aquatic plants included pollen of Nymphaceae, Alisma, and Menyanthes trifoliata L. The high concentration of microscopic charcoal particles was revealed. Gelasinospora was also found.
PAZ 2 (750–650 cm, 6050–5790 cal yr BP). Although arboreal pollen values remained high (85%–85%), tree pollen noticeably declined (to 40%) while shrubs become more abundant. Pollen values of dwarf birch (Betula nana) increased from 5%–7% to 40%–50%. The share of Picea and Abies dropped to a few percent, and the Pinus pollen value decreased to 20%–30%. The composition of herbaceous pollen and spores was similar to the previous zone, except for a lower proportion of Lycopodium annotinum (2%–3%). Menyanthes trifoliata and Typha latifolia L. were identified among the wetland plants. The concentration of microscopic charcoal particles reached its maximum value throughout the peat core. Gelasinospora was found in several samples.
PAZ 3 (650–520 cm, 5790–5370 cal yr BP). The composition of pollen assemblages in this zone was similar to PAZ 1. Tree pollen values increased to 80%–90%, mainly due to pollen of Betula alba-type. The pollen curves of Picea, Abies, and Larix formed noticeable peaks. The proportion of Betula nana reduced to 5%–10%. The concentration of microscopic charcoal gradually declined.
PAZ 4 (520–225 cm, 5370–4480 cal yr BP). Pollen assemblages are characterized by a decrease in AP to 60%–80%, and tree pollen values decreased to 40%–50%, with the exception of Pinus. At the same time, the proportion of shrubs grown as Betula nana and Alnus fruticosa increased to 30%–50% and 10%–15%, respectively. Pollen values of Pinus subgen. Haploxylon varied from 40% to 60%, and Pinus subgen. Diploxylon reached 5%–7%. Cyperaceae and Menyanthes trifoliata dominated the NAP. Pollen grains of Ephedra were found. Equisetum, Sphagnum, and bryales are common among the spores. Selaginella selaginoides (L.) Link appeared.
Fluctuations in the AP/NAP ratio and several peaks in the spore group allowed us to divide this zone into 5 subzones. Subzones 5a (520–420 cm), 5c (420–350 cm), and 5e (270–225 cm) were characterized by a decrease in tree pollen value (to 80% in subzone 5a and 5e and up to 60% in subzone 5c) and an increasing proportion of Cyperaceae, Menyanthes trifoliata (subzone 5a), Equisetum, and Polypodiaceae (subzone 4c). Arboreal pollen content increased to 90%–95% in subzone 5b (450–420 cm) and 5d (350–270 cm), mainly due to pine pollen. High peaks (200%–300% of AP + NAP) of Sphagnum mosses were detected.
PAZ 5 (225–170 cm, 4480–4220 cal yr BP). The proportion of arboreal pollen grew, Picea and Abies formed several peaks up to 10%, and the share of Betula alba pollen increased up to 50%. Cyperaceae, Saxifragaceae, and Menyanthes trifoliata were abundant in the NAP. Charcoal content was low.
PAZ 6 (170–90 cm, 4220–3600 cal yr BP). The pollen assemblages revealed the opposite tendency of the decline of tree pollen value (up to 40%–50%) and increase in Betula nana (30%–50%) and Alnus fruticosa (15%–25%). Picea, Abies, and Larix decreased significantly, while Pinus (20%–30%) and Betula (40%–50%) maintained their high proportions. NAP was scanty. Spores were represented by Equisetum (3%–5%) and single spores of Sphagnum and Lycopodium annotinum, L. clavatum.
PAZ 7 (90–45 cm, 3600–2700 cal yr BP). The pollen assemblage was characterized by the largest proportion of Abies (20%–25%) and high pollen values of Picea (10%–12%) and Pinus subgen. Haploxylon (45%–50%). Shrubs were significantly reduced (10%–12%) and represented mainly by Alnus fruticosa. The proportion of NAP and spores (mainly Poaceae, Cyperaceae, Artemisia, Valeriana, Polypodiaceae, and Equisetum) did not exceed 5%–7%.
PAZ 8 (45–0 cm, 2760 cal yr BP–present) corresponds to the uppermost layer of highly humified peat. Pollen concentration in these samples was extremely low, and pollen preservation was poor. Pollen assemblages were dominated by Pinus, Betula, shrubs, and Ericaceae. Microscopic charcoal concentration increased at the depths of 10–15 cm.
The wood fragments found during the extraction of the peat core were identified as two remains of Larix sp. (samples from depths of 825.5–830.5 cm and 832–834 cm) and two remains of Alnus fruticosa, obtained at depths of 846–847 cm and 859–860 cm.

3.3. Macroscopic Charcoal and Fire History

The reconstruction of the fire history from the macro-charcoal data is based on the hypothesis that most of the charcoal particles with a size > 125 µm were deposited between a few meters and 1–3 km away from the fire [57,68]. Long-range transport (from a distance of more than 3 km away) of macroscopic charcoal is an unlikely pathway for the particles to reach the sample plots.
Macro-charcoal concentration is high (180–670 particles cm−3) in the lower part of the peat core (851–836 cm). The highest peak of macro-charcoal concentration (up to 860 pieces cm−3, Figure 5) was detected in the lowest peat layer at the depth of 847 cm. Except for this part of the peat core, the macro-charcoal concentration did not exceed 1–10 pieces cm−3, and at several depths no charcoal particles were found.
Macro-charcoal analysis of the peat core revealed the highest CHAR value between 6200 and 5600 cal yr BP, Cint ranged from 100 to 140 pieces cm−2 yr−1 with a peak of up to 290 pieces cm−2 yr−1 at 6300 cal yr BP, and Cback varied in the interval 1–15 pieces cm−2 yr−1 (Figure 4). Thirteen fire episodes were identified, with fire return intervals (FRI) ranging from 10 to 120 years.
After 5600 cal yr BP, the accumulation of macroscopic charcoal decreased by an order of magnitude, and Cint did not exceed 10 pieces cm−2 yr−1 until the present. During the period 5600–4800 cal yr BP, Cint varied from 0 to 5 pieces cm−2 yr−1, Cback was below 0.4 pieces cm−2 yr−1, no fire episodes were identified, and FRI increased to 750 years.
A slight increase in CHAR value was observed between 4700 and 3900 cal yr BP, and Cint ranged between 0.5 and 7 pieces cm−2 yr−1. Fifteen fire episodes were identified with FRI 10–90 years. However, the low CHAR values suggest a series of low-intensity fires in the area close to the peatland. During the time interval 3900–3650 cal yr BP, the charcoal accumulation in the peatland ceased, FRI was 250 years. Between 3650 and 3550 cal yr BP, there was a short-term increase in charcoal accumulation. Cint increased to 5–7 pieces cm−2 yr−1, and Cback was about 7 pieces cm−2 yr−1 with FRI 20–25 years. After 3550 cal yr BP, charcoal input declined to insignificant values. FRI expanded to 1600 years.

4. Discussion

The results, based on the analysis of pollen and macro-charcoal from the Igarka peatland, allowed us to discuss the changes in vegetation and the history of fires in the northern Yenisei Siberia during the middle- and late-Holocene (Figure 6). Peat inception in the Igarka peatland occurred around 6320 cal yr BP during the Holocene thermal maximum. An abundance of Larix sp. and Alnus fruticosa macroremains in plant macrofossil assemblages [38] and the finding of fragments of their wood in the basal horizon of the peat sequence suggest paludification of the wet larch forest and further development of the peatland.
The Igarka pollen record showed an expansion of middle-taiga forests of Larix, Pinus sibirica, Picea, and Abies between 6320 and 5360 cal yr BP. The proportion of Larix in the pollen assemblages varied from 0.1% to 4.5%, except for a peak of up to 30% at a depth of 590 cm. According to studies on the pollen productivity of the main Arctic species [69] and the composition of surface pollen spectra from larch forests in different regions [70,71,72], Larix is strongly underestimated in pollen spectra as compared to its abundance in the vegetation. The percentage of Larix pollen in Northern Siberia rarely exceeds 3%–5% [70,73]. Relatively high pollen values of Abies and Picea indicated the tendency of climate warming and northward shift of vegetation-zone boundaries. The northern limit of the geographical range of Abies sibirica lies about 200 km south of the study area (Figure 1, [40]), and the abundance of its pollen likely indicates warmer climatic conditions. Warmer-than-present climatic conditions during the Holocene thermal maximum are suggested by the frequent occurrence of Nymphaea pollen in the assemblages. Species of Nymphaea need higher summer temperatures for growth and flowering in Siberia compared to the modern temperature conditions in the Igarka area [74].
Reconstructions of the mean July temperature in Igarka for the period 6320–5360 cal yr BP using the BMA approach showed a high variability of temperatures in the range of 14.7 to 17.3 °C with several abrupt minima (Figure 6). However, most of the values obtained showed positive temperature anomalies with respect to modern values. The reconstruction of June–July temperature on the Yamal Peninsula by dendrochronological data [75] showed an increase in summer temperatures up to 13.5 °C around 6300 cal yr BP and a progressive cooling after 5800 cal yr BP. Our results are in good agreement with the pollen-based temperature reconstructions from several lakes in the Russian Arctic, such as Lama Lake in the northwest of the Putorana Plateau [13], Levinson-Lessing Lake [12,14], and the lake around Khatanga [76] in the northern Taimyr Peninsula, that indicate a warm climate and several positive July temperature anomalies in the period between 7000 and 5000 cal yr BP. Chironomid-based temperature reconstructions, and diatom and stable isotope records from lake deposits in Yakutia [19,20,77] revealed a remarkable climate warming between ca. 6000 and 4500 cal yr BP.
Figure 6. Results of the multi-proxy analysis of the Igarka peatland, including characteristic pollen taxa, macrocharcoal accumulation rate with fire episodes, reconstructions of the mean July temperature and the mean annual precipitation compared to the Yamal June–July temperature inferred from dendrochronological data [75], and the oxygen isotope composition of diatoms from Lake Emanda (Yakutia) [77]. Pink bands indicate periods of high fire frequency.
Figure 6. Results of the multi-proxy analysis of the Igarka peatland, including characteristic pollen taxa, macrocharcoal accumulation rate with fire episodes, reconstructions of the mean July temperature and the mean annual precipitation compared to the Yamal June–July temperature inferred from dendrochronological data [75], and the oxygen isotope composition of diatoms from Lake Emanda (Yakutia) [77]. Pink bands indicate periods of high fire frequency.
Forests 14 02321 g006
The period between 6320 and 5790 cal yr BP was characterized by a high level of fire activity and an intensive accumulation of charcoal in the peat. The high concentration of micro- and macroscopic charcoal in the interval 6320–6000 cal yr BP, two orders of magnitude higher than its average content in the peat core, as well as the finding of charred plant remains and charcoal fragments by plant macrofossil analysis [38], suggest a fire adjacent to the peatland. The fire return interval ranged from 70 to 120 years and was significantly shorter than the modern interval inferred for the northern-taiga region of Central Siberia from fire scars on larch trunks [78]. The pollen record revealed a phase of abrupt decrease in tree pollen values and high abundance of Betula nana between 6050 and 5790 cal yr BP (Figure 6). Changes in pollen assemblages were more likely caused by post-fire succession of plant cover rather than vegetation dynamics caused by climatic variability. The occurrence of spores of the mainly carbonaceous fungus Gelasinospora sp. provided additional independent evidence that fires had occurred in the peatland [50,51]. We suggest that frequent forest fires without human influence may have been caused by climatic conditions, such as summer droughts. Reconstruction of mean annual precipitation using pollen data from the Igraka peatland (Figure 6) revealed a decrease in climatic wetness in 6200–5600 cal yr BP, which could contribute to higher fire frequency. A study of fire history in Northern Siberia [24,26] showed high charcoal accumulation in the mid-Holocene, which also coincides with the high charcoal accumulation rates recorded in the Lake Baikal region [27].
According to the pollen data from the Igraka peatland, the forest canopy was gradually reduced from 5360 cal yr BP; the middle-taiga vegetation was replaced by larch woodlands with spruce, pine, and some herbaceous plants that are typical for the northern taiga (Figure 6). Pinus sibirica dominates the pollen assemblages between 5360 and 4465 cal. years BP, and pollen of Pinus sylvestris is also found in small amounts (up to 5%–10%), although it is currently growing about 300 km to the south of the study area (Figure 1 in [40]). Studies of surface pollen assemblages in Northern Siberia [70,73] have shown that in sparse or open-plant communities, i.e., where the proportion of pollen transported by the wind is higher, the maximum values of both pine species are reached.
Reconstructions of July temperature at Igarka revealed three intervals of significant climate cooling in 5400–5480, 5075–4940, and 4670–4550 cal yr BP, when the temperature of the warmest month decreased to 13.5–13.7 °C. Our findings are consistent with the estimation of Yamal summer temperatures inferred from tree-ring chronologies [75], the oxygen isotope composition of diatoms from Lake Emanda [76] (Figure 6), and pollen-based climate reconstructions from Lama Lake [13] and a lake around Khatanga [75], which show a climatic deterioration after 5200–5000 cal yr BP. Paleoclimatic studies based on various proxies in Northern Eurasia show a noticeable cooling and glacial advance in mountainous areas after 5500 cal yr BP [79], apparently caused by a decrease in summer solar radiation [80].
The low recovery of macro- and micro-charcoal remains in the peat core from the Igarka mire (Figure 5) suggested a decline of fire activity in the study area, which could be an indirect sign of a humid summer. However, reconstruction of the mean annual precipitation in Igarka using the BMA technique showed relatively low values, ranging from 350 to 500 mm per year. We suggest that during the cooler and possibly shorter summers, evaporation was reduced, which could lead to an increase in soil moisture in many habitats [81], creating unfavorable conditions for the occurrence and spread of forest fires [82].
During the time interval between 4465 and 2700 cal yr BP, three phases of vegetation changes have been identified. A higher proportion of woody vegetation in the plant cover, expansion of Abies, and the increase in Picea abundance in forest stands occurred in 4465–4200 and 3600–2700 cal yr BP, indicating climate warming and a shift northward of the boundary between the middle- and northern-taiga. Biomass burning increased and FRI became shorter, but the low value of charcoal input (Figure 5 and Figure 6) suggests low-intensity fires in the area adjacent to the Igarka peatland. Frequent fires may promote local permafrost thawing, creating better conditions for tree growth and regeneration [83], and likely favoring the expansion of spruce and fir species. The reduction of the forest canopy and the expansion of birch and shrubs (Alnus fruticosa, Betula nana), apparently caused by climate cooling, were detected in 4200–3600 cal yr BP.
Reconstructions of the July temperature at Igarka show a number of positive and negative anomalies for summer temperatures, most of which agree well with pollen data, but, in some intervals, the reconstructed summer temperature contradicts vegetation changes inferred from pollen records. Inconsistencies between pollen and climate reconstructions can be explained by the weaknesses of the BMA approach in the situation of limited modern pollen assemblages [62]. Nevertheless, the phase of southern-taiga corresponded to the increase in July temperature to 16.9–17.2 °C between 3620–3300 cal yr BP and the phase of the remarkable reduction of forest canopy in 3860–3670 cal yr BP corresponded to the climate cooling and the temperature drop to 14.9 °C. Our results are largely in agreement with chironomid-based July temperature reconstructions from two mountain lakes in the western part of the Putorana Plateau [84], which suggest a warmer climate between 3900 and 3400 cal yr BP than at present and a subsequent cooling with the maximum at 2500 cal yr BP. Paleoclimatic records based on pollen from Lama and Levinson-Lessing lakes [13,14] showed several positive temperature anomalies for July between 4700 and 3600 cal yr BP. Reconstruction of Yamal June-July temperatures from tree-ring records revealed a high variability of summer conditions with a pronounced mid-to-late Holocene cooling trend [75].
After 2700 cal yr BP, the vegetation cover of the study area becomes very similar to the modern pattern. Pollen assemblages show a gradual decrease in Picea, Abies, and Larix pollen values, while the proportion of pine, dwarf birch, and shrubs increases, indicating an expansion of northern-taiga woodlands. However, since the uppermost part of the peat sequences was obviously partly destroyed by water erosion and forest fires, and the sampling resolution for the last 2700 years was low, the chronology for the last ca. 1800 years is unclear, which did not allow us to reconstruct vegetation changes in detail.
Climate change since ca. 2700 cal yr BP was evidenced by numerous proxy data from Siberian Arctic regions [12,75,76,77,83,84,85], Yakutia [76], and data from a global scale [86]. The clearly manifested cooling trend was revealed from dendroclimatological reconstruction and analysis of the frequency of abnormal anatomical structures in the larch and spruce wood from the Yamal peninsula [87]. Time-coeval pollen data from the peatland at Igarka near the study site [39] indicated the degradation of the dark coniferous taiga and the expansion of sparse larch-birch woodlands and shrub communities formed mainly by Betula nana and Alnus fruticosa. Pollen records from the more northerly coastal regions of the Taymyr Peninsula [13] and even further to the northeast, including the coastal regions of the Eastern Arctic seas [88] also testify to the stabilization of vegetation-zone boundaries around 2500 cal yr BP. Further vegetation changes were apparently caused by local peat development processes, wildfires, and human impact.

5. Conclusions

The new high-resolution pollen and charcoal data from the perennial frost mound in the peatland near the town of Igarka provide a unique opportunity to investigate the mid- to-late Holocene forest and fire history in this very remote and poorly documented area of Yenisei Siberia. Our findings suggest several phases of vegetation change between 6320 and 2700 cal yr BP, influenced by climatic fluctuations and fire occurrence. During the Holocene thermal maximum and the periods of warming (6320–5360, 4465–4200, and 3600–2700 cal yr BP), the eastern margin of the West Siberian Lowland was occupied by middle-taiga larch forests with a high proportion of Abies sibirica, Picea obovata, and Pinus sibirica. Climate warming caused a northward shift of the vegetation-zone boundaries in the Yenisei Siberia. The area of distribution of Abies sibirica expanded by 200 km northward compared to its modern range. Fire frequencies and biomass burning increased during the warming periods. We suggest that the frequent fires may encourage the melting of the local permafrost, thereby enhancing tree growth and regeneration, and likely favoring the expansion of Abies sibirica and Picea obovata farther to the north.
Climate deterioration at 5400–5480, 5075–4940, 4670–4550, and 3860–3670 cal yr BP led to a degradation of the dark coniferous forests in the study area. This was caused by the expansion of sparse larch-birch woodlands with an admixture of Picea obovata and Pinus sibirica and shrub communities dominated by Betula nana and Alnus fruticosa. The cooling of the climate was accompanied by a decrease in the frequency of fires.
Although the uppermost part of the studied peat sequences was partly destroyed by water erosion and wildfires and the sampling resolution was low, we assume that the vegetation pattern of the region became close to the modern one at around 2700 cal. yr BP. Based on the comparison of modern environmental processes with periods of climate warming and increased fire activity in the past, we suggest a potential increase in suitable habitats for tree growth in Yenisei Siberia in the future, and further studies are needed to test this hypothesis.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/f14122321/s1, S1. R Code for the modern analogue technique.

Author Contributions

Investigation, E.N., O.R., N.M., D.K., R.A., A.S., M.K. and A.P.; data curation, R.A., D.K. and A.P.; writing—original draft preparation, E.N.; writing—review and editing, E.N. and A.O. All authors have read and agreed to the published version of the manuscript.

Funding

Field works: radiocarbon dating, charcoal, and pollen analysis were supported by the Russian Science Foundation (grant number 20-17-00043). Reconstructions of climate changes and fire history were supported by the State assignment FMGE-2019-0005. Data analysis and paper preparation were funded by Megagrant project (agreement 075-15-2021-599, 8 June 2021). The analysis of climate anomaly—fire frequency interaction conducted by A. Olchev was supported by the Russian Science Foundation (grant number 22-17-00073).

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Acknowledgments

The authors are very grateful to colleagues from Igarka Geocryological Laboratory and Melnikov Institute of Permafrost SB RAS for appreciable help in field work.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 2. Views of the peatland and its forest environment: (a). The Igarka peatland, top view; (b). the Igarka peatland and perennial frost mounds, the red arrow indicates the core sampling site; (c). forest surrounding the peatland.
Figure 2. Views of the peatland and its forest environment: (a). The Igarka peatland, top view; (b). the Igarka peatland and perennial frost mounds, the red arrow indicates the core sampling site; (c). forest surrounding the peatland.
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Figure 3. Bacon R script age-depth model (red dotted line), random walks (grayscale), and 95% CI (dotted gray lines) of twenty radiocarbon dates (distributions in blue) and parameter settings (red text at top right) for the peat core from the Igarka peatland (modified after Novenko et al. [38]).
Figure 3. Bacon R script age-depth model (red dotted line), random walks (grayscale), and 95% CI (dotted gray lines) of twenty radiocarbon dates (distributions in blue) and parameter settings (red text at top right) for the peat core from the Igarka peatland (modified after Novenko et al. [38]).
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Figure 4. Percentage pollen diagram of the Igarka peatland. Pollen sum: AP + NAP; additional curves represent ×10 exaggeration of base curves; black dots indicate the presence of taxa <1%).
Figure 4. Percentage pollen diagram of the Igarka peatland. Pollen sum: AP + NAP; additional curves represent ×10 exaggeration of base curves; black dots indicate the presence of taxa <1%).
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Figure 5. Temporal variability of macroscopic charcoal concentration, charcoal accumulation rate in the Igarka peatland, and fire return interval. Red + indicates fire episodes.
Figure 5. Temporal variability of macroscopic charcoal concentration, charcoal accumulation rate in the Igarka peatland, and fire return interval. Red + indicates fire episodes.
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Table 1. Radiocarbon dating of the peat from the Igarka peatland.
Table 1. Radiocarbon dating of the peat from the Igarka peatland.
Laboratory Code IGANAMSDepth, cmMaterial 14C yr. BP, 1σAge, cal. yr. BP,
2σ (Probability)
835415TOC 11930 ± 201817–1896 (0.806)
833250TOC3230 ± 203391–3468 (0.965)
833360TOC3320 ± 203480–3574 (0.987)
8334101TOC3430 ± 203617–3723 (0.820)
8335150TOC3805 ± 204144–4248 (0.874)
8336202TOC4120 ± 204528–4654 (0.545)
8337252TOC4080 ± 204518–4624 (0.793)
8338301TOC4320 ± 204840–4888 (0.797)
8339351TOC4360 ± 204857–4973 (1.000)
8340402TOC4445 ± 204962–5070 (0.549)
8341449TOC4340 ± 204851–4960 (1.000)
8342500TOC4490 ± 205155–5288 (0.569)
8343550TOC4830 ± 205574–5596 (0.582)
8344599TOC4955 ± 255601–5729 (1.000)
8345650TOC4315 ± 254837–4888 (0.772)
8346700TOC5165 ± 205900–5942 (0.827)
8347749TOC5200 ± 205916–5994 (1.000)
8348798TOC5400 ± 206187–6282 (0.954)
8349845TOC5425 ± 206198–6287 (1.000)
8350860TOC5500 ± 206276–6315 (0.898)
1 TOC—total organic carbon.
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Novenko, E.; Rudenko, O.; Mazei, N.; Kupriyanov, D.; Andreev, R.; Shatunov, A.; Kusilman, M.; Prokushkin, A.; Olchev, A. Effects of Climate Change and Fire on the Middle and Late Holocene Forest History in Yenisei Siberia. Forests 2023, 14, 2321. https://doi.org/10.3390/f14122321

AMA Style

Novenko E, Rudenko O, Mazei N, Kupriyanov D, Andreev R, Shatunov A, Kusilman M, Prokushkin A, Olchev A. Effects of Climate Change and Fire on the Middle and Late Holocene Forest History in Yenisei Siberia. Forests. 2023; 14(12):2321. https://doi.org/10.3390/f14122321

Chicago/Turabian Style

Novenko, Elena, Olga Rudenko, Natalia Mazei, Dmitriy Kupriyanov, Rodion Andreev, Anton Shatunov, Maria Kusilman, Anatoly Prokushkin, and Alexander Olchev. 2023. "Effects of Climate Change and Fire on the Middle and Late Holocene Forest History in Yenisei Siberia" Forests 14, no. 12: 2321. https://doi.org/10.3390/f14122321

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