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Proceeding Paper

Carbon Stocks, Sequestration Rate and Efficiency over 50 Years of Increasing Mineral N Fertilization †

by
Elmira Saljnikov
1,2,*,
Nikola Koković
1,
Tara Grujić
1,
Ljubomir Životić
3,
Sonja Tošić Jojević
1,
Vojislav Lazović
1 and
Goran Jačimović
4
1
Institute of Soil Science, Teodora Drajzera 7, 11000 Belgrade, Serbia
2
Mitscherlich Academy for Soil Fertility (MITAK), Prof.-Mitscherlich-Allee 1, 14641 Paulinenaue, Germany
3
Faculty of Agriculture, University of Belgrade, Njemanjina 6, 11080 Belgrade-Zemun, Serbia
4
Faculty of Agriculture Novi Sad, University of Novi Sad, Sq. Dositeja Obradovića 8, 21000 Novi Sad, Serbia
*
Author to whom correspondence should be addressed.
Presented at the 3rd International Electronic Conference on Agronomy, 15–30 October 2023; Available online: https://iecag2023.sciforum.net/.
Biol. Life Sci. Forum 2023, 27(1), 7; https://doi.org/10.3390/IECAG2023-15756
Published: 1 November 2023
(This article belongs to the Proceedings of The 3rd International Electronic Conference on Agronomy)

Abstract

:
Microbially mediated soil organic matter is an extremely sensitive pool that indicates subtle changes in the quality parameters. The calculation of different carbon pools (organic carbon—OC, labile carbon—PMC, light carbon—LFC and microbial carbon—MBC), their sequestration rate (Csr) and efficiency (Cse), as affected by 50 yrs. of mineral fertilization, was carried out. The C sequestration rates between the fertilized plots were not significantly different except for the control plot. The sensitivity index, which indicates the response of soil organic matter to changes in different carbon fractions, demonstrated a strong correlation with the amount of light-fraction organic matter (OM). The use of mineral N over 50 years resulted in increase of soil labile C, but did not result in greater C sequestration efficiency. The results give a deeper insight into the behavior of carbon pools and can serve as a reliable basis for further studies focused on neutral carbon emissions and effective C sequestration.

1. Introduction

Soil organic carbon (SOC) sequestration in agricultural soil is directly affected by anthropogenic activities and climate change; both can alter net primary production (NPP) and organic matter decomposition [1]. Under the same climatic, soil and topographic conditions, the biomass and activity of soil microorganisms are the main conductors of SOM mineralization and CO2 fluxes. Generally, long-term fertilization adversely affects the soil microbial community [2,3]. Microbially mediated soil organic matter is an extremely sensitive pool that indicates subtle changes in the quality parameters responsible for the soil’s ecological and productive functions. However, the accumulation of organic carbon in soil is a slow and reversible process. In contrast, the annual fresh plant litter decomposes during one growing season, thus returning organic carbon into the atmosphere as a carbon dioxide. In Serbia, agricultural production is still largely based on traditional land management. In previous works, we outlined the effect of the long-term application of synthetic fertilizers on various soil properties and parameters [3,4]. In these studies, it was found that increasing the dose of synthetic nitrogen naturally led to an increase in the yield, and thus, also in the biomass of plant residues. The latter found that labile carbon pools also increased. The purpose of this work was to establish how increasing the doses of synthetic nitrogen may or may not contribute to carbon sequestration.

2. Materials and Methods

In a field experiment lasting more than 50 years, four variants of different doses of mineral fertilizers with increasing doses of nitrogen and equal doses of phosphorus and potassium fertilizers were selected and compared with a control that did not receive either synthetic or organic fertilizers. The detailed description of the study site and experimental design can be found in the study by [3]. The soil type was Eutric Cambisol, and the area is located in central Serbia (44°24′58″ N and 20°10′34″ E). The plots were arranged in a randomized block design in four replications.
Soil respiration was measured by the alkali trap method under controlled laboratory conditions (temperature—28 °C, and soil moisture—50% WHC) at the following intervals: 3, 9, 16, 30, 44, 62, and 83 days for each treatment in four replications. The potentially mineralizable carbon (PMC) and mineralization rate constant (k) were calculated using the first-order kinetic model (Exponential Rise to Maximum; SPSS Inc.: Chicago, IL, USA; Sigma Plot 14). The microbial biomass carbon (MBC) was determined by the fumigation–incubation method [5]. The light fraction C (LFC) was determined in a CNS atomic analyzer after isolation based on the density separation with a NaI solution [6].
The carbon stocks (Mg/ha) of SOC, LFC, PMC and MBC as well as the carbon sequestration rate CSR (Mg/ha/y) and carbon sequestration efficiency CSE (%) for each fraction of carbon were calculated as described in [7].

3. Results and Discussion

In general, with an increase in the dose of mineral nitrogen, all the studied carbon pools increased accordingly (Table 1). A significant difference was observed between the control and all fertilized treatments, as well as between the lower and higher doses of N. Higher doses of mineral nutrition produce higher plant biomass, both aboveground and belowground [3]. The long-term accumulation of crop residues as an easily available organic substrate resulted in a greater accumulation of labile fractions of SOM under N120 and N150 treatments. Generally, the prolonged use of synthetic fertilizer can adversely affect soil biota [2,3]. However, when soil samples were placed in controlled conditions with optimal moisture and temperature, the microbes began to grow actively. This in turn led to high levels of labile carbon pools. In addition, autumn samples contain significantly more labile fractions of organic matter that return after harvesting.
In contrast to the concentrations of the labile C pools, their reserves did not differ significantly, except for the control and the lowest dose of N (N60) (Table 2). Hence, delta carbon stocks showed the same trend.
Calculations of the rate and efficiency of carbon sequestration for each carbon pools showed that, in general, there was no significant difference between the treatments with increasing doses of mineral N (Table 3) for LFC and MBC, while OC and PMC showed less sequestration efficiency at the lowest dose (N60) of mineral N compared to N120 and N150.
This study confirmed that long-term field experiments provide a highly reliable basis for setting realistic targets for carbon sequestration in traditionally managed agricultural landscapes. Although the addition of higher doses of mineral nitrogen has increased the concentration of labile carbon pools over 50 years, it has not been able to effectively sequester carbon. This research provides greater insight into the carbon cycle and sequestration potential of a traditional agricultural system that uses only synthetic fertilizers.

Author Contributions

Conceptualization, E.S. and N.K.; methodology, T.G.; software, V.L.; validation, G.J. and E.S.; formal analysis, S.T.J.; investigation, N.K. and T.G.; resources, N.K.; data curation, L.Ž.; writing—original draft preparation, E.S.; writing—review and editing, L.Ž.; visualization, V.L.; supervision, G.J.; project administration, S.T.J.; funding acquisition, N.K. All authors have read and agreed to the published version of the manuscript.

Funding

The Ministry of Science, Technological Development and Innovation of the Republic of Serbia [grant number 451-03-47/2023-01/200011].

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Available upon request.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Yan, X.; Cai, Z.; Wang, S.; Smith, P. Direct measurement of soil organic carbon content change in the croplands of China. Global Change Biol. 2010, 17, 1487–1496. [Google Scholar] [CrossRef]
  2. Huang, L.; Riggins, C.W.; Villamil, M.B.; Rodríguez-Zas, S.; Zabaloy, M.C. Long-term N fertilization imbalances potential N acquisition and transformations by soil microbes. Sci. Total Environ. 2019, 691, 562–571. [Google Scholar] [CrossRef] [PubMed]
  3. Koković, N.; Saljnikov, E.; Eulenstein, F.; Čakmak, D.; Buntić, A.; Sikirić, B.; Ugrenović, V. Changes in Soil Labile Organic Matter as Affected by 50 Years of Fertilization with Increasing Amounts of Nitrogen. Agronomy 2021, 11, 2026. [Google Scholar] [CrossRef]
  4. Koković, N.; Jačimović, G.; Sikirić, B.; Čirić, V.; Ugrenović, V.; Zhapparova, A.; Saljnikov, E. Changes in Eutric Cambisol due to long-term mineral fertilization: A case study in Serbia. Ital. J. Agron. 2022, 17, 2029. [Google Scholar] [CrossRef]
  5. Jenkinson, D.S.; Powlson, D.S. The effect of biocidal treatments on metabolism in soil–V: A method for measuring soil biomass. Soil Biol. Biochem. 1976, 8, 209–213. [Google Scholar] [CrossRef]
  6. Janzen, H.H.; Compbell, C.A.; Brandt, S.A.; Lafond, G.P.; Townley-Smith, L. Light-fraction organic matter in soils from long-term crop rotation. Soil Sci. Soc. Am. J. 1992, 56, 1799–1806. [Google Scholar] [CrossRef]
  7. Xiang, Y.; Cheng, M.; Wen, Y.; Darboux, F. Soil Organic Carbon Sequestration under Long-Term Chemical and Manure Fertilization in a Cinnamon Soil, Northern China. Sustainability 2022, 14, 5109. [Google Scholar] [CrossRef]
Table 1. Labile fractions of soil organic matter.
Table 1. Labile fractions of soil organic matter.
TreatmentFertilizerOC, %LFC mg/kgPMC, mg/kgMBC, mg/kgqCO2
control00.92 b ± 0.02332.44 a913.91 a188.31 a3.664 a
N60N60P51K670.98 b ± 0.02589.55 b1287.95 b228.66 b4.562 b
N90N90P51K671.08 c ± 0.03590.69 b1893.50 c295.91 c5.694 c
N120N120P51K671.13 c ± 0.03650.16 c1840.94 c342.99 d4.743 b
N150N150P51K671.14 c ± 0.02680.49 c2054.64 c352.14 d5.331 c
t-test ************
p < 0.05p < 0.05p < 0.001p < 0.001p < 0.05
Note: ** Significantly different at p < 0.01; *** Significantly different at p < 0.001 values followed by the same letter in a column are not significantly different; OC—organic carbon; LFC—light fraction carbon; PMC—potentially mineralizable carbon; MBC—microbial biomass carbon; qCO2—microbial metabolic quotient.
Table 2. Carbon stocks in different fractions.
Table 2. Carbon stocks in different fractions.
TreatmentCarbon Stock, t/haΔ Carbon Stock, t/ha
OCPMCLFCMBCOCPMCLFCMBC
01.0585 a1.1058 a0.4023 a0.2279 a
N60P80K801.2110 b1.5584 a0.7134 b0.2767 a0.1524 a0.0355 a0.0247 a0.0037 a
N90P80K801.2639 b2.2911 b0.7147 b0.3581 ab0.2054 b0.0959 b0.0253 a0.0105 b
N120P80K801.2756 b2.2275 b0.7867 b0.4150 b0.2171 b0.0924 b0.0317 ab0.0154 b
N150P80K801.2917 b2.4861 b0.8234 b0.4261 b0.2332 b0.1134 b0.0346 ab0.0163 b
Note: values followed by the same letter in a column are not significantly different.
Table 3. Carbon sequestration rate and efficiency.
Table 3. Carbon sequestration rate and efficiency.
TreatmentCsr, Mg/ha/yrCse, %
OCPMCLFCMBCOCPMCLFCMBC
N60P80K800.3049 a0.0710 a0.0494 a0.0075 a0.07664 a0.07848 a0.07934 a0.07680 a
N90P80K800.4109 a0.1917 b0.0505 a0.0210 b0.05541 ab0.08088 ab0.08085 a0.08080 a
N120P80K800.4343 a0.1848 b0.0634 a0.0309 b0.03822 b0.08237 b0.08241 a0.08252 a
N150P80K800.4665 ba0.2268 b0.0693 ba0.0327 b0.03983 b0.08216 b0.08226 a0.08238 a
Note: Csr—carbon sequestration rate, Mg/ha/year; Cse—carbon sequestration efficiency, %. The same letter within a column signifies no statistical difference.
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MDPI and ACS Style

Saljnikov, E.; Koković, N.; Grujić, T.; Životić, L.; Tošić Jojević, S.; Lazović, V.; Jačimović, G. Carbon Stocks, Sequestration Rate and Efficiency over 50 Years of Increasing Mineral N Fertilization. Biol. Life Sci. Forum 2023, 27, 7. https://doi.org/10.3390/IECAG2023-15756

AMA Style

Saljnikov E, Koković N, Grujić T, Životić L, Tošić Jojević S, Lazović V, Jačimović G. Carbon Stocks, Sequestration Rate and Efficiency over 50 Years of Increasing Mineral N Fertilization. Biology and Life Sciences Forum. 2023; 27(1):7. https://doi.org/10.3390/IECAG2023-15756

Chicago/Turabian Style

Saljnikov, Elmira, Nikola Koković, Tara Grujić, Ljubomir Životić, Sonja Tošić Jojević, Vojislav Lazović, and Goran Jačimović. 2023. "Carbon Stocks, Sequestration Rate and Efficiency over 50 Years of Increasing Mineral N Fertilization" Biology and Life Sciences Forum 27, no. 1: 7. https://doi.org/10.3390/IECAG2023-15756

APA Style

Saljnikov, E., Koković, N., Grujić, T., Životić, L., Tošić Jojević, S., Lazović, V., & Jačimović, G. (2023). Carbon Stocks, Sequestration Rate and Efficiency over 50 Years of Increasing Mineral N Fertilization. Biology and Life Sciences Forum, 27(1), 7. https://doi.org/10.3390/IECAG2023-15756

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