Calculation of the critical loads for acidity and nitrogen levels on arable Fluvisol

Authors

  • Tsetska Simeonova Institute of Soil Science, Agrotechnology and Plant Protection “Nikola Pushkarov” – Sofia, Agricultural Academy Author https://orcid.org/0000-0003-0668-3538
  • Irena Atanassova Institute of Soil Science, Agrotechnology and Plant Protection “Nikola Pushkarov” – Sofia, Agricultural Academy Author https://orcid.org/0000-0002-6969-769X
  • Maya Benkova Institute of Soil Science, Agrotechnology and Plant Protection “Nikola Pushkarov” – Sofia, Agricultural Academy Author https://orcid.org/0000-0002-4305-3220
  • Maria Mihaylova Institute of Soil Science, Agrotechnology and Plant Protection “Nikola Pushkarov” – Sofia, Agricultural Academy Author

DOI:

https://doi.org/10.61308/MGDI3153

Keywords:

critical load, nitrogen, base cations, input-output

Abstract


This paper aims to estimate the maximum nutrient nitrogen input, called critical load that will balance the system in the stability limits regarding soil acidification while also not limiting plant growth as a result of mass balance calculation. The assessment was made on the basis of data obtained during a 4-years (2020-2023) field experiment and changes in the major input-output pools of nitrogen and base cations as a result of changing N loads. The study was carried out on Fluvisol, near Plovdiv in Southern Bulgaria under a cereal crop rotation. The experiment design included four N rates (T0-control, T1 N100, T2 N140, T3 N180) for wheat (Triticum aestivum L.) and (T1 N120, T2 N160, T3 N200) kg/ha for maize (Zea mays L.) respectively. Results show that average amount of N added by atmospheric deposition and irrigation water for the period 2020-2023 ranged from 10 to 24 kg.ha-1. Depositions of Ca2+ and Mg2+ via rainfall was reaching to 42 kg.ha-1 Ca2+ and 15.9 kg.ha-1 Mg. The average amount of N leached out of the control treatment (reaching 4.5 kg.ha-1 N) was four to five times lower in comparison with fertilized treatments T2 and T3. It was established that when using criteria - pH of the soil the critical load for acidifying N for this soil type was considerably high (170-227 kg.ha-1 per year) in case of maize. A significant reduction in the critical load for acidifying N was registered after wheat when irrigation was not applied (31-82 kg.ha-1 per year).

 

References

Arinushkina, E. (1970). Guidelines in Chemical Soil Analysis, Izd. MGU, Moskow, 487 (Ru).

Dechert, G., Veldkamp, E. & Brumme, R. (2005). Are Partial Nutrient Balances Suitable to Evaluate Nutrient Sustainability of Land use Systems? Results from a Case Study in Central Sulawesi, Indonesia. Nutrient Cycling in Agroecosystems, 72(3), 201-212, doi: https://doi.org/10.1007/S10705-005-1546-2.

Delon, C., Galy-Lacaux, C., Barret, B., Ndiaye, O., Serça, D., Guérin, F., ... & Probst, A. (2022). Nitrogen budget and critical load determination at a Sahelian grazed grassland site. Nutrient Cycling in Agroecosystem, 124, 17-34, doi: https://doi.org/10.1007/s10705-022-10220-6.

De Vries, W, Posh, M., Sverdup, H. U., Larssen, T., de Wit, H. A., Bobbink, R. & Hettelingh, J.P. (2015). Geochemical Indicators for Use in the Computation of Critical Loads and Dynamic Risk Assessments. In: de Vries, W., Hettelingh, J.P., Posch, M. (eds). Critical Loads and Dynamic Risk Assessments. Environmental Pollution, 25. Springer, 1–11, Dordrecht, doi: https://doi.org/10.1007/978-94-017-9508-1_2.

De Vries, W. (1991). Methodologies for the assessment and mapping of critical loads and the impact of abatement of strategies on forest soils. Report 46, Wageningen: The Winand Staring Centre for Integrated Land, Soil, and Water Research.

De Vries, W. (1993.) Average critical loads for nitrogen and sulphur and its use in acidification abatement policy in the Netherlands. Water, Air, and Soil Pollution, 68, 399-434, doi: https://doi.org/10.1007/BF00478466.

De Vries, W., Kros, H., Reinds, G. J., Wamelink, W., Mol, J., van Dobben, H., ... & Hettelingh, J. P. (2007). Developments in deriving critical limits and modelling critical loads of nitrogen for terrestrial ecosystems in Europe. https://edepot.wur.nl/38943 (last accessed 03.10.2025).

Erisman, J.W., Grennfelt, P. & Sutton, M. (2003). The European perspective on nitrogen emission and deposition. Environment International, 29(2-3), 311-325, doi: https://doi.org/10.1016/S0160-4120(02)00162-9.

Erisman, J.W., van Grinsven, H., Leip, A., Mosier, A. & Bleeker, A. (2010). Nitrogen and biofuels, an overview of the current state of knowledge. Nutrient Cycling in Agroecosystems, 86, 211-223, doi: https://doi.org/10.1007/s10705-009-9285-4.

Freer-Smith, P. H. & Kennedy, F. (2003). Base cation removal in harvesting and biological limit terms for use in the simple mass balance equation to calculate critical loads for forest soils. Water, Air, and Soil Pollutant, 145, 409-427, doi: https://doi.org/10.1023/A:1023615004433.

Georgieva, E., Hristova, E., Syrakov, D., Prodanova, M., Gospodinov, I., & Veleva, B. (2022). Sulfur and Nitrogen Depositions in BULGARIA—Model Results and Observations. Atmosphere, 13(2), 343, doi: https://doi.org/10.3390/atmos13020343.

Gerassimova, I., Nenov, M., Simeonova, Ts., Nazarkov, M., & Petkova, Z. (2024). Fertilization and maize yields in a four-year cycle crop rotation under various soil and climatic conditions. Journal of Central European Agriculture, 25(4), 1098-1106, doi: https://jcea.agr.hr/en/issues/article/4338.

Grieve, I. C. (2001). Human activities on soil properties and their implications for the soil systems in Scotland. Catena, 432(2-4), 361-374, doi: https://doi.org/10.1016/S0341-8162(00)00147-8.

Guo, J. H., Liu, X. J., Zhang, Y., Shen, J. L., Han, W. X., Zhang, W. F., ... & Zhang, F. S. (2010). Significant Acidification in Major Chinese Croplands. Science, 327 (5968), 1008-1010, doi: 10.1126/science.1182570.

Hao, T., Zhu, Q., Zeng, M., Shen, J., Shi, X., Liu, X., ... & de Vries, W. (2020). Impacts of nitrogen fertilizer type and application rate on soil acidification rate under a wheat-maize double cropping system. Journal of Environmental Management, 270, doi: https://doi.org/10.1016/j.jenvman.2020.110888.

Ignatova, N., Yorova, K., Grozeva, M., Trendafilov, K., Tinchev, G. & Petkova, T. (1998). Methodological guidelines for calculation of critical loads for acidity, sulphur and nitrogen for the soils in Bulgaria, Sofia, p. 45 (Bg).

IUSS Working Group WRB (2015). World Reference Base for Soil Resources 2014, Update 2015. International Soil Classification System for Naming Soils and Creating Legends for Soil Maps. World Soil Resources Reports No. 106, Rome: FAO.

Kemmitt, S.J., Wright, D., Goulding, K.W.T. & Jones D.L. (2006.) pH regulation of carbon and nitrogen dynamics in two agricultural soils. Soil Biology and Biochemistry, 38(5), 898-911, doi: https://doi.org/10.1016/j.soilbio.2005.08.006.

Koleva V. (2002). Assessment of critical nitrogen loads on alluvial meadow soil. Doctoral dissertation. Nikola Pushkarov Institute of Soil Science, Sofia 2002 (Bg).

Koleva, V., Stoicheva, D., Donov, D. & Stoichev, D. (2003). Long-term mass balance on arable Fluvisol for determination of critical nitrogen loads in terms of soil acidification. Bulgarian Journal of Agricultural Science, 9(4), 435-448: https://www.agrojournal.org/09/013.htm (Bg) (last accessed 19.09.2025).

Liu, Y., Zhang, M., Li, Y., Zhang, Y., Huang, X., Yang, Y., Zhu, H., Xiong, H. & Jiang, T. (2023). Influence of Nitrogen Fertilizer Application on Soil Acidification Characteristics of Tea Plantations in Karst Areas of Southwest China. Agriculture, 13(4), 849, doi: https://doi.org/10.3390/agriculture13040849.

Małecki, J. J., Matyjasik, M., Krogulec, E. & Porowska, D. (2022). Long-term trends and factors influencing rainwater chemistry in the Tatra Mountains. Poland. Geology, Geophysics and Environment, 48(1), 19-38. doi: https://doi.org/10.7494/geol.2022.48.1.19.

Nilsson, J. & Grennfelt, P. (1988) Critical Loads for Sulphur and Nitrogen. Report from Skokloster Workshop. Skokloster, doi: https://doi.org/10.1007/978-94-009-4003-1_11.

Oenema, O. & Roest, C.W.J. (1998). Nitrogen and Phosphorus Losses from Agriculture into Surface Waters; The Effects of Policies and Measures in the Netherlands. Water Science and Technology, 37(2), 19-30, doi: https://doi.org/10.1016/S0273-1223(98)00052-3.

Page, A.L., Miller, R.H. & Keeney, D.R. eds. (1982), Methods of Soil Analysis: Part 2. Chemical and microbiological properties, II edition, ASA and SSSA (Publ), Madison, Wisconsin, USA, 1184, doi:10.2134/agronmonogr9.2.2ed.

Peterburgskii, A.V. (1986). Practical Guidance on Agro-chemistry. Kolos Publ. house, Moscow (Ru).

Posch, M. Aherne, J. & Hettelinght, J.P. (2011). Nitrogen critical loads using biodiversity-related critical limits. Environmental Pollution, 159(10), 2223-222, doi: https://doi.org/10.1016/j.envpol.2010.11.001.

Reinds, G.J., Posch, M., de Vries, W., Slootweg, J. & Heeteling, H-J. (2008). Critical Loads of Sulphur and Nitrogen for Terrestrial Ecosystems in Europe and Northern Asia Using Different Soil Chemical Criteria. Water, Air, and Soil Pollutant, 193, 269-287, doi: https://doi.org/10.1007/s11270-008-9688-x.

Růžek, M., Myška, O., & Oulehle, F. (2019). Input-Output Budgets of Nutrients in Adjacent Norway Spruce and European Beech Monocultures Recovering from Acidification. Forests, 10(1), 68, doi: https://doi.org/10.3390/f10010068.

Schlecht, E. & Hiernaux, R. (2004). Beyond adding inputs and outputs: process assessment and upscaling in modelling nutrient flows. Nutrient Cycling in Agroecosystems, 70, 303-319, doi: 10.1007/s10705-005-0765-x.

Simeonova, Ts., Stoicheva, D. & Alexandrova, P. (2015). Ecological problems and nitrogen balance in vegetable crops growing. Eurasian Journal of Soil Science, 4(1), 62-68, doi: 10.18393/ejss.03607.

Simeonova, Ts. & Nenova, L. (2023). Dynamics of the chemical composition of precipitation an input of elements in an agricultural area in Southern Bulgaria, Bulgaria. Journal of Soil Science, 2(8), 104-112, doi: https://doi.org/10.5281/zenodo.10207564 (Bg).

Simeonova, Ts., Nenova, L., Benkova, M. & Atanassova, I. (2023). Nitrogen balance at the maize cultivation in Southern Bulgaria under anthropogenic loading. Bulgarian Journal of Agricultural Science, 29(6) 2023, 1049-1056 (Bg).

Spranger, T., Lorenz, U., & Gregor, H-D., (Eds). (2004). Manuel on methodologies and criteria for modelling and mapping critical levels & loads and air pollution effects, risks and trends. Chapter V. Mapping critical loads. Umweltbundesamt, ISSN 0722-186X, p.V, 1- 73.

Stoichev, D. (1974). A device to obtain lysimetric water. Soil Science and Agrochemistry, 9(5), 13-18. (Bg).

Stoichev, D. (1989). Effect of long-term fertilization on pH values, and available nitrogen, phosphorus and potassium in the soil, In: Proc. from 4th National Conference on Soil science, “Soil science problems under the conditions of intensive agriculture”, Sofia, 404-410. (Bg).

Stoichev, D. (1997). Some ecological aspects of the anthropogenic loading on the soils. Dr Sc. Dissertation, Nikola Pushkarov Institute of Soil Science, Sofia, (Bg).

Sverdrup, H. & de Vries, W. (1994). Calculating critical loads for acidity with the simple mass balance method. Water, Air, and Soil Pollutant, 72, 143-162, doi: https://doi.org/10.1007/BF01257121.

Sverdrup, H. & Warfvinge, P. (1993). The effect of soil acidification on the growth of trees, grass and herbs as expressed by the (Ca + Mg + K)/Al ratio. Reports in Ecology and Environmental Engineering 2, Department of Chemical Engineering II, Lund University, Lund, Sweden, 177.

UBA, (1996). Manual on methodologies and criteria for mapping critical levels/loads and geographical areas where they are exceeded, 1996. UN/ECE CLRTAP Task Force on Mapping and the CCE. Umweltbundesamt, Berlin, Germany.

Waldner, P., Thimonier, A., Graf Pannatier, E., Etzold, S., Schmitt, M., Marchetto, A. & Minaya, M. (2015). Exceedance of critical loads and of critical limits impacts tree nutrition across Europe. Annals of Forest Science, 72, 929-939, doi: https://doi.org/10.1007/s13595-015-0489-2.

Watmough, S. A. (2024) Critical loads for alkalization in terrestrial ecosystems. Science of The Total Environment, 927, Article 171967, doi: https://doi.org/10.1016/j.scitotenv.2024.171967.

Xu., D, Ros., H, Zhu., Q, Xu., M, Men., S, Cai., Z, Zhang., F. & de Vries., W. (2024). Major drivers of soil acidification over 30 years differ in paddy and upland soils in China. Science of The Total Environment, 916, Article, doi: 10.1016/j.scitotenv.2024.170189.

Zhao Y, Duan L, Larssen T, Mulder J, Hu L. & Hao J. (2007). Calculating critical loads for acidification for five forested catchments in China using an extended steady state function. Science of the Total Environment, 387(1-3), 54-67, doi: 10.1016/j.scitotenv.2007.07.014.

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Published

23-12-2025

How to Cite

Calculation of the critical loads for acidity and nitrogen levels on arable Fluvisol. (2025). Bulgarian Journal of Soil Science, Agrochemistry and Ecology, 59(4), 45-57. https://doi.org/10.61308/MGDI3153