Elena D. Lapshina

Prof. Dr. Elena D. Lapshina

Department of Environmental Dynamics and Global Climate Change, Yugra State University, ul. Chekhova 16, 628012 Khanty-Mansiysk, Russia

Research Focus & Metrics

Academic Career Length

23Years (2004-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 September 2005 in Nature
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MWMartin Joseph Wassen
Martin Joseph Wassen
HVHarry Olde Venterink
Harry Olde Venterink
Elena D. LapshinaElena D. Lapshina
Elena D. Lapshina
FTFranziska Tanneberger
Franziska Tanneberger

19 March 2018 in Nature Communications
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JPJaan Pärn
Jaan Pärn
JVJos T. A. Verhoeven
Jos T. A. Verhoeven
KBKlaus Butterbach-Bahl
Klaus Butterbach-Bahl
NDNancy B. Dise
Nancy B. Dise
SUSami Ullah
Sami Ullah
Ülo ManderÜlo Mander
Ülo Mander
Nitrous oxide (N2O) is a powerful greenhouse gas and the main driver of stratospheric ozone depletion. Since soils are the largest source of N2O, predicting soil response to changes in climate or land use is central to understanding and managing N2O. Here we find that N2O flux can be predicted by models incorporating soil nitrate concentration (NO3−), water content and temperature using a global field survey of N2O emissions and potential driving factors across a wide range of organic soils. N2O emissions increase with NO3− and follow a bell-shaped distribution with water content. Combining the two functions explains 72% of N2O emission from all organic soils. Above 5 mg NO3−-N kg−1, either draining wet soils or irrigating well-drained soils increases N2O emission by orders of magnitude. As soil temperature together with NO3− explains 69% of N2O emission, tropical wetlands should be a priority for N2O management.

1 January 2007 in Tellus B: Chemical and Physical Meteorology
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MRM. E. Repo
M. E. Repo
JHJ . T. Huttunen
J . T. Huttunen
ANA. V. Naumov
A. V. Naumov
ACA. V. Chichulin
A. V. Chichulin
Elena D. LapshinaElena D. Lapshina
Elena D. Lapshina
PMP. J . Martikainen
P. J . Martikainen
Release of CO 2 and CH 4 from small wetland lakes in western Siberia

3 April 2008 in Ecosystems
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MEMaarten B. Eppinga
Maarten B. Eppinga
MRMax Rietkerk
Max Rietkerk
WBWiebe Borren
Wiebe Borren
Elena D. LapshinaElena D. Lapshina
Elena D. Lapshina
WBWladimir Bleuten
Wladimir Bleuten
MWMartin Joseph Wassen
Martin Joseph Wassen
Regular spatial patterns of sharply bounded ridges and hollows are frequently observed in peatlands and ask for an explanation in terms of underlying structuring processes. Simulation models suggest that spatial regularity of peatland patterns could be driven by an evapotranspiration-induced scale-dependent feedback (locally positive, longer-range negative) between ridge vegetation and nutrient availability. The sharp boundaries between ridges and hollows could be induced by a positive feedback between net rate of peat formation and acrotelm thickness. Theory also predicts how scale-dependent and positive feedbacks drive underlying patterns in nutrients, hydrology, and hydrochemistry, but these predictions have not yet been tested empirically. The aim of this study was to provide an empirical test for the theoretical predictions; therefore, we measured underlying patterns in nutrients, hydrology, and hydrochemistry across a maze-patterned peatland in the Great Vasyugan Bog, Siberia. The field data corroborated predicted patterns as induced by scale-dependent feedback; nutrient concentrations were higher on ridges than in hollows. Moreover, diurnal dynamics in water table level clearly corresponded to evapotranspiration and showed that water levels in two ridges were lower than in the hollow in between. Also, the data on hydrochemistry suggested that evapotranspiration rates were higher on ridges. The bimodal frequency distribution in acrotelm thickness indicated sharp boundaries between ridges and hollows, supporting the occurrence of a positive feedback. Moreover, nutrient content in plant tissue was most strongly associated with acrotelm thickness, supporting the view that positive feedback further amplifies ridge–hollow differences in nutrient status. Our measurements are consistent with the hypothesis that the combination of scale-dependent and positive feedback induces peatland patterning.

2 November 2016 in Applied Vegetation Science
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TPTomáš Peterka
Tomáš Peterka
MHMichal Hájek
Michal Hájek
MJMartin Jiroušek
Martin Jiroušek
BJBorja Jiménez‐Alfaro
Borja Jiménez‐Alfaro
LALiene Aunina
Liene Aunina
MCMilan Chytrý
Milan Chytrý

20 January 2004 in Quaternary Research
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WBWiebe Borren
Wiebe Borren
WBWladimir Bleuten
Wladimir Bleuten
Elena D. LapshinaElena D. Lapshina
Elena D. Lapshina
Although recent studies have recognized peatlands as a sink for atmospheric CO2, little is known about the role of Siberian peatlands in the global carbon cycle. We have estimated the Holocene peat and carbon accumulation rate in the peatlands of the southern taiga and subtaiga zones of western Siberia. We explain the accumulation rates by calculating the average peat accumulation rate and the long-term apparent rate of carbon accumulation (LORCA) and by using the model of Clymo (1984, Philosophical Transactions of the Royal Society of London Series B 303, 605–654). At three key areas in the southern taiga and subtaiga zones we studied eight sites, at which the dry bulk density, ash content, and carbon content were measured every 10 cm. Age was established by radiocarbon dating. The average peat accumulation rate at the eight sites varied from 0.35 ± 0.03 to 1.13 ± 0.02 mm yr−1 and the LORCA values of bogs and fens varied from 19.0 ± 1.1 to 69.0 ± 4.4 g C m−2 yr−1. The accumulation rates had different trends especially during the early Holocene, caused by variations in vegetation succession resulting in differences in peat and carbon accumulation rates. The indirect effects of climate change through local hydrology appeared to be more important than direct influences of changes in precipitation and temperature. River valley fens were more drained during wetter periods as a result of deeper river incision, while bogs became wetter. From our dry bulk density results and our age–depth profiles we conclude that compaction is negligible and decay was not a relevant factor for undrained peatlands. These results contribute to our understanding of the influence of peatlands on the global carbon cycle and their potential impact on global change.