<p>The mineralization of soil organic carbon (SOC) is typically enhanced following the incorporation of straw into the soil, and liming for acidic soil is recognized as effective practice to improve soil pH, which also could affect SOC mineralization. However, it is not well understood whether straw and lime together suppress, enhance, or have no net effect on native SOC mineralization relative to single application, and the mechanisms involved remain unclear. Therefore, in conjunction with a <sup>13</sup>C stable isotope tracing method, a 60-day incubation study was carried out for two acidic paddy soils under four treatments: control (CK), dolomite alone (D), straw alone (S), and dolomite plus straw (D + S). Dolomite or straw application individually induced positive priming effects, increasing SOC mineralization by 14.2–29.2% and 15.2–19.5%, respectively. In contrast, their combined application (D + S) significantly suppressed native SOC mineralization by 18.1–31.7% (negative priming) while enhancing straw-derived CO<sub>2</sub> emissions. Dolomite application significantly raised soil pH value. Additionally, D, S, as well as D + S treatments increased dissolved organic C (DOC) but decreased NH<sub>4</sub><sup>+</sup>-N, consequently altering the activities of endo-β-1,4-glucanase and cellobiohydrolase (both involved in cellulose degradation) and laccase (involved in lignin degradation), as well as the absolute abundances of corresponding genes of GH48 (regulating endo-β-1,4-glucanase), <i>cbhI</i> (regulating cellobiohydrolase), and LMCO (regulating laccase-like copper monooxidase). Structural equation modeling showed that SOC mineralization was directly regulated by DOC and mineral nitrogen, and indirectly by soil pH value. Collectively, combined dolomite and straw returning alleviated soil acidity, reduces SOC mineralization loss, and promoted straw decomposition, offering a promising strategy for C sequestration and sustainable management in acidic paddy field regions.</p>

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Dolomite in conjunction with straw application increased straw-derived CO2 emission while depressed soil organic carbon mineralization in two acidic paddy soils

  • Peng Xu,
  • Hongtao Wu,
  • Mengdie Jiang,
  • Tao Jin,
  • Bo Zhu,
  • Zhangyong Liu,
  • Hongyu Lin,
  • Ronggui Hu

摘要

The mineralization of soil organic carbon (SOC) is typically enhanced following the incorporation of straw into the soil, and liming for acidic soil is recognized as effective practice to improve soil pH, which also could affect SOC mineralization. However, it is not well understood whether straw and lime together suppress, enhance, or have no net effect on native SOC mineralization relative to single application, and the mechanisms involved remain unclear. Therefore, in conjunction with a 13C stable isotope tracing method, a 60-day incubation study was carried out for two acidic paddy soils under four treatments: control (CK), dolomite alone (D), straw alone (S), and dolomite plus straw (D + S). Dolomite or straw application individually induced positive priming effects, increasing SOC mineralization by 14.2–29.2% and 15.2–19.5%, respectively. In contrast, their combined application (D + S) significantly suppressed native SOC mineralization by 18.1–31.7% (negative priming) while enhancing straw-derived CO2 emissions. Dolomite application significantly raised soil pH value. Additionally, D, S, as well as D + S treatments increased dissolved organic C (DOC) but decreased NH4+-N, consequently altering the activities of endo-β-1,4-glucanase and cellobiohydrolase (both involved in cellulose degradation) and laccase (involved in lignin degradation), as well as the absolute abundances of corresponding genes of GH48 (regulating endo-β-1,4-glucanase), cbhI (regulating cellobiohydrolase), and LMCO (regulating laccase-like copper monooxidase). Structural equation modeling showed that SOC mineralization was directly regulated by DOC and mineral nitrogen, and indirectly by soil pH value. Collectively, combined dolomite and straw returning alleviated soil acidity, reduces SOC mineralization loss, and promoted straw decomposition, offering a promising strategy for C sequestration and sustainable management in acidic paddy field regions.