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Amino acid-sulphur decomposition in agricultural soil profile along a long-term recultivation chronosequence. / Wang, Qiqi; Bauke, Sara L; Wang, Deying et al.
In: Science of the Total Environment, Vol. 951, 15.11.2024, p. 175409.

Research output: Contribution to journalArticlepeer-review

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Wang, Q, Bauke, SL, Wang, D, Zhao, Y, Reichel, R, Jones, DL, Chadwick, DR, Tietema, A & Bol, R 2024, 'Amino acid-sulphur decomposition in agricultural soil profile along a long-term recultivation chronosequence', Science of the Total Environment, vol. 951, pp. 175409. https://doi.org/10.1016/j.scitotenv.2024.175409

APA

Wang, Q., Bauke, S. L., Wang, D., Zhao, Y., Reichel, R., Jones, D. L., Chadwick, D. R., Tietema, A., & Bol, R. (2024). Amino acid-sulphur decomposition in agricultural soil profile along a long-term recultivation chronosequence. Science of the Total Environment, 951, 175409. https://doi.org/10.1016/j.scitotenv.2024.175409

CBE

MLA

VancouverVancouver

Wang Q, Bauke SL, Wang D, Zhao Y, Reichel R, Jones DL et al. Amino acid-sulphur decomposition in agricultural soil profile along a long-term recultivation chronosequence. Science of the Total Environment. 2024 Nov 15;951:175409. Epub 2024 Aug 13. doi: 10.1016/j.scitotenv.2024.175409

Author

Wang, Qiqi ; Bauke, Sara L ; Wang, Deying et al. / Amino acid-sulphur decomposition in agricultural soil profile along a long-term recultivation chronosequence. In: Science of the Total Environment. 2024 ; Vol. 951. pp. 175409.

RIS

TY - JOUR

T1 - Amino acid-sulphur decomposition in agricultural soil profile along a long-term recultivation chronosequence

AU - Wang, Qiqi

AU - Bauke, Sara L

AU - Wang, Deying

AU - Zhao, Yi

AU - Reichel, Rüdiger

AU - Jones, Davey L

AU - Chadwick, David R

AU - Tietema, Albert

AU - Bol, Roland

N1 - Copyright © 2024 The Authors. Published by Elsevier B.V. All rights reserved.

PY - 2024/11/15

Y1 - 2024/11/15

N2 - The significance of sulphur (S) availability for crop yield and quality is highlighted under the global S deficiency scenario. However, little is known about the temporal trend in belowground organic S mineralisation when restoring land to productive agricultural systems, particularly for the deeper soil parts. Therefore, we investigated the decomposition of 35S-labelled methionine in surface (0-30 cm) and subsurface soil (30-60 cm and 60-90 cm) over a 48-year recultivation chronosequence (sampled after1, 8, 14, 24 and 48 years). Soil total sulphur (TS) significantly (p < 0.05) increased in surface soil but not in subsurface soils after 48 years of recultivation. Overall, the immobilisation of 35S-methionine (35S-MB) in subsurface soils relative to year 1 significantly decreased over the chronosequence but did not change in the surface samples. The 35S-MB values in subsurface soils were positively corrected with soil carbon (C) stoichiometry (Pearson correlation, p < 0.05), suggesting the immobilisation of methionine was likely constrained by microbial C demand in deep soil. Compared to year 1, 35S-SO42- released from 35S-methionine significantly declined throughout the older (≥ 8 years) soil profiles. Significant (p < 0.05) changes in the organic 35S partition (35S immobilisation and 35S released as sulphate) were observed in year 8 after the soil was recultivated with N-fixing alfalfa or fertilisers. Whereas, after that (≥ 14 years), soil organic S partition remained affected when conventional tillage and agricultural crops dominated this site. Indicating that the effect of recultivation on organic S decomposition depends on the manner of recultivation management. Our study contributes to an improved understanding of amino acid S and organic S mineralisation under severe anthropogenic disturbance.

AB - The significance of sulphur (S) availability for crop yield and quality is highlighted under the global S deficiency scenario. However, little is known about the temporal trend in belowground organic S mineralisation when restoring land to productive agricultural systems, particularly for the deeper soil parts. Therefore, we investigated the decomposition of 35S-labelled methionine in surface (0-30 cm) and subsurface soil (30-60 cm and 60-90 cm) over a 48-year recultivation chronosequence (sampled after1, 8, 14, 24 and 48 years). Soil total sulphur (TS) significantly (p < 0.05) increased in surface soil but not in subsurface soils after 48 years of recultivation. Overall, the immobilisation of 35S-methionine (35S-MB) in subsurface soils relative to year 1 significantly decreased over the chronosequence but did not change in the surface samples. The 35S-MB values in subsurface soils were positively corrected with soil carbon (C) stoichiometry (Pearson correlation, p < 0.05), suggesting the immobilisation of methionine was likely constrained by microbial C demand in deep soil. Compared to year 1, 35S-SO42- released from 35S-methionine significantly declined throughout the older (≥ 8 years) soil profiles. Significant (p < 0.05) changes in the organic 35S partition (35S immobilisation and 35S released as sulphate) were observed in year 8 after the soil was recultivated with N-fixing alfalfa or fertilisers. Whereas, after that (≥ 14 years), soil organic S partition remained affected when conventional tillage and agricultural crops dominated this site. Indicating that the effect of recultivation on organic S decomposition depends on the manner of recultivation management. Our study contributes to an improved understanding of amino acid S and organic S mineralisation under severe anthropogenic disturbance.

U2 - 10.1016/j.scitotenv.2024.175409

DO - 10.1016/j.scitotenv.2024.175409

M3 - Article

C2 - 39142402

VL - 951

SP - 175409

JO - Science of the Total Environment

JF - Science of the Total Environment

SN - 0048-9697

ER -