Japan Geoscience Union Meeting 2025

Presentation information

[E] Poster

M (Multidisciplinary and Interdisciplinary) » M-IS Intersection

[M-IS05] Environmental, Socio-economic, and Climatic Changes in Northern Eurasia

Sun. May 25, 2025 5:15 PM - 7:15 PM Poster Hall (Exhibition Hall 7&8, Makuhari Messe)

convener:Pavel Groisman(NC State University Research Scholar at NOAA National Centers for Environmental Information, Asheville, North Carolina, USA), Shamil Maksyutov(National Institute for Environmental Studies), Alexander Olchev(Lomonosov Moscow State University, Moscow, Russia)

5:15 PM - 7:15 PM

[MIS05-P09] Soil organic carbon turnover in the meadow ecosystems of drained peatland (Tarmanskoe Fen, Western Siberia)

*Evgeniya Soldatova1, Elizaveta Plotnikova1 (1.Institute of Forest Science of the Russian Academy of Sciences)

Keywords:delta13C, isotopic approach , natural abundance, pasture, hayfield, rewetting

Evaluation of soil organic carbon (SOC) turnover rate is crucial for assessment of the measures targeted greenhouse gas (GHG) flux reduction and boosting C sequestration especially with drained wetlands. Drained wetlands are often subjected to rewetting for biodiversity restoration and climate change mitigation however the influence of such measures on GHG emission and C sequestration is debatable. We chose seven points in drained eutrophic Tarmanskoe Fen (south of the Western Siberia) subjected by the peat extraction in 70-80th of XX century. There were four groups of points: 1. site naturally rewetted after peat extraction without reclamation due to earth surface decrease and degradation of drainage system; 2. point in the meadow which are occasionally used as a hayfield, and probably as a pasture and arable land; 3. the meadow which is used as a pasture and hayfield by local residents about 40 years. 4. Unoccupied meadows. The turnover rate of SOC was estimated based on stable isotope signatures (δ13C) down to 70 cm of the soil profile depth because the slope of the linear regression between δ13C and the logarithm of SOC is a proxy of SOM turnover (Acton et al., 2013; Powers and Schlesinger, 2002). Commonly, the SOC content logarithmically depends on depth, whereas the final 13C fractionation increases with the number of C cycles and with the intensity and completeness of the SOM processing according to the Rayleigh distillation. The regressions between the Lg-transformed SOC content and δ13C have negative linear trends. The negative slope (βC) of the linear regression between Lg SOC and δ13C corresponds to the relative rate of C turnover (Wynn et al., 2006, 2005). Greater absolute values of βC refer to higher relative SOC turnover rate. Content of SOC was measured by element analyzer varioPYROcube and δ13C was determined by isotope ratio mass-spectrometer isoprime precisION coupled with element analyzer varioISOTOPEcube (Elementar, UK) after removal of carbonates from soil sample by HCl fumigation. Surprisingly, we found that the rewetted plot has the highest SOC turnover rate compared to unoccupied meadows, hayfields and pastures (Fig. 1). However, all of the βC values have the same order of absolute magnitude, near unity, which means relatively close SOC turnover within all studied plots. Only TMB-2 showed the βC values close to zero and lowest SOC turnover rate. Correlation analysis showed that SOC turnover rate increases with SOC content in upper 30 cm of soil profile (rs 0.81, p<0.05) and decreases with soil compaction (with increasing of density (rs -0.74, p<0.05)). The connection with soil humidity is absent. It reflects faster loss of organic carbon from residual peat horizons and means that rewetting in this case do not prevent this process. Relative rate of SOC turnover also positively correlated with C content in aboveground biomass of the studied plots (rs 0.83, p<0.05) which can be a sign that more productive meadow ecosystems loss more organic carbon due to microbial respiration.
Research was supported by the Russian Science Foundation (No 23-77-10012).
References
Acton, P., Fox, J., Campbell, E., Rowe, H., Wilkinson, M., 2013. Carbon isotopes for estimating soil decomposition and physical mixing in well-drained forest soils. J. Geophys. Res. Biogeosciences 118, 1532–1545.
Powers, J.S., Schlesinger, W.H., 2002. Geographic and vertical patterns of stable carbon isotopes in tropical rain forest soils of Costa Rica. Geoderma 109, 141–160.
Wynn, J.G., Bird, M.I., Wong, V.N.L., 2005. Rayleigh distillation and the depth profile of 13C/12C ratios of soil organic carbon from soils of disparate texture in Iron Range National Park, Far North Queensland, Australia. Geochim. Cosmochim. Acta 69, 1961–1973.
Wynn, J.G., Harden, J.W., Fries, T.L., 2006. Stable carbon isotope depth profiles and soil organic carbon dynamics in the lower Mississippi Basin. Geoderma 131, 89–109.