Seasonal Dynamics of Organic Carbon and Nitrogen in Biomasses of Microorganisms in Arable Mollisols Affected by Different Tillage Systems

Yuriy S. Kravchenko, Xingyi Zhang, Chunyu Song, Wei Hu, Anna V. Yarosh and Olena V. Voitsekhivska
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Yuriy S. Kravchenko: Soil Science and Soil Conservation Department, National University of Life and Environmental Sciences of Ukraine, 15, Heroyiv Oborony Street, 03041 Kyiv, Ukraine
Xingyi Zhang: Northeast Institute of Geography and Agricultural Ecology, 138 Harping RD, Harbin 150081, China
Chunyu Song: Northeast Institute of Geography and Agricultural Ecology, 138 Harping RD, Harbin 150081, China
Wei Hu: Northeast Institute of Geography and Agricultural Ecology, 138 Harping RD, Harbin 150081, China
Anna V. Yarosh: Soil Science and Soil Conservation Department, National University of Life and Environmental Sciences of Ukraine, 15, Heroyiv Oborony Street, 03041 Kyiv, Ukraine
Olena V. Voitsekhivska: Institute of Biology and Medicine, Taras Shevchenko National University of Kyiv, Volodymyrska St., 64/13, 01601 Kyiv, Ukraine

Land, 2022, vol. 11, issue 4, 1-21

Abstract: Tillage has been reported to induce seasonal changes of organic carbon (C micro ) and nitrogen (N micro ) in the biomass of microorganisms. Soil microorganisms execute such ecosystem functions as it is an immediate sink of labile biophil elements; it is an agent of a conversion, catalysis and synthesis of humus substances; it transforms soil contaminants into nonhazardous wastes and it participates in soil aggregation and pedogenesis as a whole. However, the seasonal turnover of microorganisms on arable lands in temperate ecosystems has not been studied at a relevant level. Hence, we are aimed at studying the dynamics of such soil microbial biomass patterns as C micro , N micro , microbial index (MI = (C micro /C TOC )·100%) and CO 2 -C emissions against the background of 9 years of tillage and 22 years of abandoned (Ab) and fallow (F) usage. Our study was conducted on a long-term experimental site on a Mollisol in Northeast China. The maximum C micro and N micro contents were recorded at the beginning of the growing season at the 0–10-cm layer and mid-July at the 20–40-cm layer, while the minimum content was during August–October. The C micro content ranged from 577.79 to 381.79 mg −1 kg −1 using Ab in the spring to 229.53 to 272.86 mg −1 kg −1 in the autumn using CT (conventional tillage) and F in the 0–10- and 10–20-cm layers, respectively. The amplitude of N micro content changes were several times lower as compared with the C micro . The smallest quartile range (IQR 0.25–0.75 ) of such changes was shown when using the following treatments: no till (NT) and Ab in the 0–10-, NT and F in the 10–20- and CT in the 20–40-cm layer. The widest C micro :N micro ratio was recorded at F and CT in the 0–20- and CT and rotational tillage (Rot) in the 20–40-cm layer. The MI dynamics were similar to the trends of C micro and N micro and changed from 0.72 ± 0.168 to 2.00 ± 0.030%. The highest share of C micro in C TOC was at Ab (1.82 ± 1.85%) and NT (1.66 ± 1.52 %) in the 0–10-, Ab (1.23 ± 1.27%) and NT (1.29 ± 1.32%) in the 10–20- and Ab (1.19 ± 1.09%) and F (1.11 ± 1.077%) in the 20–40-cm layer, correspondingly. The Pearson’s correlation coefficient between C micro and C TOC increased from the upper 0–10- to the lower 20–40-cm layer; it was “strong” and “high” between C micro and C TOC . Different uses of Mollisol affected the amplitude of the C micro and N micro seasonal changes, but it did not change their trend. Our results suggest the key role of Ab and NT technologies in C micro accumulation in the total organic carbon (TOC).

Keywords: Mollisol; soil organic matter; microorganisms; microbial index; crop growing season (search for similar items in EconPapers)
JEL-codes: Q15 Q2 Q24 Q28 Q5 R14 R52 (search for similar items in EconPapers)
Date: 2022
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