EGU26-17172, updated on 14 Mar 2026
https://doi.org/10.5194/egusphere-egu26-17172
EGU General Assembly 2026
© Author(s) 2026. This work is distributed under
the Creative Commons Attribution 4.0 License.
Oral | Wednesday, 06 May, 12:18–12:28 (CEST)
 
Room 0.11/12
Short-term carbon dynamics from ¹³C‑labelled maize residue and its derived biochar in long‑term NPK and NPK plus biochar amended soil
Sobia Bibi1,2, Barira Shoukat Hafiza1,2, Wolfgang Wanek2, Magdeline Vlasimsky1, Mariana Vezzone1, Janice Nakamya3, Maria Heiling1, Gerd Dercon1, Taru Sandén4, Rebecca Hood-Nowotny3, and Adelheid Spiegel4
Sobia Bibi et al.
  • 1International Atomic Energy Agency, Soil and Water Management and Crop Nutrition Laboratory, Joint FAO/IAEA Centre of Nuclear Techniques in Food and Agriculture, Department of Nuclear Sciences and Applications, Seibersdorf, Austria
  • 2University of Vienna, Department of Microbiology and Ecosystem Science, Division Terrestrial Ecosystem Research, Vienna, Austria
  • 3Institute of Soil Research, University of Natural Resources and Life Sciences (BOKU), Vienna, Austria
  • 4Austrian Agency for Health and Food Safety – (AGES), Institute for Sustainable Plant Production, Department for Soil Health and Plant Nutrition, Vienna, Austria

Enhancing soil organic carbon (SOC) in croplands is fundamental to climate‑smart agriculture (CSA), yet the mechanisms by which labile and recalcitrant carbon (C) inputs build and stabilize SOC remain unclear. Crop residues supply labile C that improve microbial activity and particulate organic matter (POM) formation, whereas biochar is considered a recalcitrant, negative‑emission amendment. This study used ¹³C‑labelled maize crop residues and its derived biochar, applied at 1.5% w/w (1.46 atom% ¹³C) to trace amendment-derived C into different soil C pools such as particulate organic C (POC), mineral-associated organic C (MAOC), microbial biomass C (MBC), and microbial respiration. Soil was sampled (Grabenegg, Austria) from two long-term management practices: one fertilized with mineral NPK since 1954 (SM1) and one receiving the same NPK regime plus wood‑derived biochar since 2022 (SM2). In a 44‑day laboratory incubation we quantified how the laboratory amendment of 13C-crop residue and 13C-biochar, alone and interacting with the long-term soil management practices, affect microbial utilization and C stabilization.

The results showed that field biochar treated soil (SM2) had higher SOC (by 51%) than non-biochar amended field soil (SM1), indicating that longer-term biochar application enhanced soil C stocks. In the short-term, at day 44 of the incubation, SOC under laboratory applied biochar was highest in both soils (SM1: 21.1g C kg-1; SM2: 26.8 g C kg-1), followed by crop residue (SM1: 15.2 g C kg-1; SM2: 21.1 g C kg-1), compared to soil with no laboratory C amendment (SM1: 11.8 g C kg-1; SM2: 17.8 g C kg-1). This highlights that in the short-term SOC gains were higher for biochar (SOC gains of 9.0-9.3 g C kg-1) than for crop residue (SOC gains of 3.0-3.3 g C kg-1). In addition, both soils showed a strong positive relationship between SOC and POC (R² = 0.783) but not with MAOC, indicating that SOC increases were largely driven by changes in the POM. The 13C tracing will allow to partition and follow the amendment-derived allocation of C into microbial biomass, respiratory use, and the transfer from the POC into the MAOC pool by microbial turnover (data evaluation ongoing). Overall, biochar proved to be the most effective CSA amendment for enhancing SOC in both long-term and in the short-term.

How to cite: Bibi, S., Hafiza, B. S., Wanek, W., Vlasimsky, M., Vezzone, M., Nakamya, J., Heiling, M., Dercon, G., Sandén, T., Hood-Nowotny, R., and Spiegel, A.: Short-term carbon dynamics from ¹³C‑labelled maize residue and its derived biochar in long‑term NPK and NPK plus biochar amended soil, EGU General Assembly 2026, Vienna, Austria, 3–8 May 2026, EGU26-17172, https://doi.org/10.5194/egusphere-egu26-17172, 2026.