

Features of the behavior of the antibiotic tetracycline hydrochloride in the soil environment
https://doi.org/10.31089/1026-9428-2025-65-7-477-483
EDN: lrikcj
Abstract
Introduction. Pollution of the environment with tetracycline is caused by both emissions from pharmaceutical production and the introduction of antibiotic residues with manure as fertilizer, which requires the development of methods for cleaning, monitoring the content and studying the stability of the substance in the soil to reduce environmental risks.
The study aims to investigate the stability of tetracycline and the determination of its transformation products in the soil environment.
Materials and methods. Preparation of standard tetracycline solutions and their loading into the soil. Extraction of tetracycline from soil with EDTA-McIlwain buffer followed by purification by solid phase extraction. Analysis of extracts by chromatography with tandem mass spectrometry for quantitative and qualitative determination of the starting material and its transformation products. Comparative analysis of mass spectra of soil extracts to identify new decomposition products and assess the rate of degradation.
Results. In soil, tetracycline undergoes gradual transformation with a half-life of 5–7 days for sod-podzolic soil and 8–12 days for chernozem; at the same time, decarboxamidation, deamination and dehydroxylation products accumulate, and researchers have also discovered previously undescribed compounds (m/z 679 and 701) with a suspected dimeric structure. Regardless of the type of soil, the composition of the transformation products was the same, which indicates similar mechanisms of antibiotic decomposition in different soil conditions.
Limitations. The authors conducted the study in laboratory conditions using artificially contaminated soil samples, which may not fully reflect the complexity and diversity of real soil ecosystems and natural tetracycline transformation processes. They studied only two types of soil (sod-podzolic and chernozem), while in nature there is a much greater variety of soils with different physico-chemical properties that can significantly affect the rate and nature of the breakdown of the antibiotic. Experts identified the decay products only from mass spectrometric data without confirming their structure using additional methods (for example, NMR-spectroscopy), which leaves the possibility of erroneous interpretation of the composition of the products.
Conclusions. Tetracycline decomposes rapidly in the soil to form new transformation products, including previously undescribed ones, which can significantly affect environmental safety and requires further study of their properties and consequences for the environment.
Ethics. The study does not require the provision of an opinion from the biomedical Ethics Committee or other documents.
Contributions:
Antropova N.A. — collecting and processing material, performing experimental work, writing text, editing;
Streletskiy A.V. — concept and design of research, collection and processing of material, experimental work, statistical processing, text writing, editing;
Ushakova O.V. — research concept and design, editing;
Yudin S.M. — editing.
Funding. The study was conducted with financial support as part of a government assignment.
Conflict of interest. The authors declare no conflict of interest.
Received: 29.07.2025 / Accepted: 02.08.2025 / Published: 05.09.2025
About the Authors
Natalia S. AntropovaRussian Federation
Junior Researcher of the Department of Physical and Chemical Research and Ecotoxicology
e-mail: NAntropova@cspfmba.ru
Alexey V. Streletskiy
Russian Federation
Senior Researcher of the Department of Physical and Chemical Research and Ecotoxicology, Cand. of Sci. (Chem.)
e-mail: AStreletsky@cspfmba.ru
Olga V. Ushakova
Russian Federation
Leading Researcher of the Hygiene Department, Cand. of Sci. (Med.)
Sergey M. Yudin
Russian Federation
Acting Director General, Dr. of Sci. (Med.), Professor
References
1. Forsberg K.J., Reyes A., Wang B., Selleck E.M., Sommer M.O., Dantas G. The shared antibiotic resistome of soil bacteria and human pathogens. Science. 2012; 337(6098): 1107–11. https://doi.org/10.1126/science.1220761
2. Wu X.L., Xiang L., Yan Q.Y., Jiang Y. N., Li Y. W., Huang X. P., et al. Distribution and risk assessment of quinolone antibiotics in the soils from organic vegetable farms of a subtropical city, Southern China. Sci. Total Environ. 2014; 487: 399–406. https://doi.org/10.1016/j.scitotenv.2014.04.015
3. Lavrukhina O.I., Amelin V.G., Kish L.K., Tretyakov A.V., Pen’kov T.D. Determination of Residual Amounts of Antibiotics in Environmental Samples and Food Products. Zhurnal analiticheskoj khimii. 2022; 77(11): 969–1015. https://doi.org/10.31857/S004445022211007X (in Russian).
4. Wegst-Uhrich S.R., Navarro D.A., Zimmerman L., Aga D.S. Assessing antibiotic sorption in soil: a literature review and new case studies on sulfonamides and macrolides. Chem. Cent. J. 2014; 8(1):5. https://doi.org/10.1186/1752-153X-8-5
5. Wang F., Wang Z., Zhao Y., Zhang J. Performance of Traditional and Emerging Water-Treatment Technologies in the Removal of Tetracycline Antibiotics. Catalysts. 2024; 14(4): 269. https://doi.org/10.3390/catal14040269
6. Xu H., Mi H.Y., Guan M.M., Shan H.Y., Fei Q., Huan Y.F. et al. Residue analysis of tetracyclines in milk by HPLC coupled with hollow fiber membranes-based dynamic liquid-liquid micro-extraction. Food Chem. 2017; 232: 198–202. https://doi.org/10.1016/j.foodchem.2017.04.021
7. Lebedinets S., Vakh C., Cherkashina K., Pochivalov A., Moskvin L., Bulatov A. Stir membrane liquid phase microextraction of tetracyclines using switchable hydrophilicity solvents followed by high-performance liquid chromatography. J. Chromatogr. A. 2020; 1615: 460743. https://doi.org/10.1016/j.chroma.2019.460743
8. Nekrasova L.P., Kuleshova O.J. Determination of antibiotics of the tetracycline group in water by high-performance liquid chromatography on a diode matrix detector with preliminary concentration by solid-phase extraction. Gigiena i sanitariya. 2024; 103(3): 266–272. https://doi.org/10.47470/0016-9900-2024-103-3-266-272 (in Russian).
9. Castillo-García M.L., Aguilar-Caballos M.P., Gómez-Hens A. A europium- and terbium-coated magnetic nanocomposite as sorbent in dispersive solid phase extraction coupled with ultra-high performance liquid chromatography for antibiotic determination in meat samples. J. Chromatogr. A. 2015; 1425: 73-80. https://doi.org/10.1016/j.chroma.2015.11.048
10. Wang K., Lin K., Huang X., Chen M. A simple and fast extraction method for the determination of multiclass antibiotics in eggs using LC-MS/MS. J. Agric. Food Chem. 2017; 65(24): 5064–5073. https://doi.org/10.1021/acs.jafc.7b01777
11. Karaca S., Kabil E., Akmehmet Balcıoğlu I. Quantification of multi-class antibiotics by UHPLC–MS/MS analysis combined with salt-assisted acetonitrile extraction: comparative evaluation of dairy and poultry manure. International Journal of Environmental Analytical Chemistry. 2018; 98(13): 1186–1206. https://doi.org/10.1080/03067319.2018.1541986
12. Antropova N.S., Ushakova O.V., Savostikova O.N., Filimonova E.I. Problems Related to Antibiotic Pollution of the Environment: A Review with a Focus on Tetracyclines. Zdorov'e naseleniya i sreda obitaniya – ZNiSO. 2024; 32(3): 33–43. https://doi.org/10.35627/2219-5238/2024-32-3-33-43 (in Russian).
13. Akimenko Ju.V., Kolesnikov S.I., Kazeev K.Sh. Ecologically safe concentrations of antibiotics in ordinary chernozems. Zhivye i biokosnye sistemy. 2023; 45. https://doi.org/10.18522/2308-9709-2023-45-4 (in Russian).
14. Scaria J., Anupama K.V., Nidheesh P.V. Tetracyclines in the environment: An overview on the occurrence, fate, toxicity, detection, removal methods, and sludge management. Sci. Total Environ. 2021; 771: 145291. https://doi.org/10.1016/j.scitotenv.2021.145291
15. Ahmad F., Zhu D., Sun J. Environmental fate of tetracycline antibiotics: degradation pathway mechanisms, challenges, and perspectives. Environ. Sci. Eur. 2021; 33(1): 64. https://doi.org/10.1186/s12302-021-00505-y
16. Wang Z., Li Y., Wang J., Li S. Tetracycline antibiotics in agricultural soil: Dissipation kinetics, transformation pathways, and structure-related toxicity. Sci. Total Environ. 2024; 949: 175126. https://doi.org/10.1016/j.scitotenv.2024.175126
17. Koba O., Golovko O., Kodešová R., Fér M., Grabic R. Antibiotics degradation in soil: A case of clindamycin, trimethoprim, sulfamethoxazole and their transformation products. Environ Pollut. 2017; 220(Pt B): 1251–1263. https://doi.org/10.1016/j.envpol.2016.11.007
18. Wen-li Zh., Li-fang Zh., Ke-yu Zh., Xiao-yang W., Fei‑qun X. Determination of Tetracyclines and Their Epimers in Agricultural Soil Fertilized with Swine Manure by Ultra-High-Performance Liquid Chromatography Tandem Mass Spectrometry. J. Integrative Agriculture. 2012; 11(7): 1189–1198. https://doi.org/10.1016/S2095-3119(12)60114-2
19. Cycoń M., Mrozik A., Piotrowska-Seget Z. Antibiotics in the soil environment — degradation and their impact on microbial activity and diversity. Frontiers in microbiology. 2019; 10: 338. https://doi.org/10.3389/fmicb.2019.00338
20. Tetracyclines. Chemical Encyclopedia: in 5 volumes. Chief editor N.S. Zefirov. Moscow: Bol'shaja Rossijskaja Jenciklopedija; 1995; 4: 639.
21. Conde-Cid M., Núñez-Delgado A., Fernández-Sanjurjo M. J., Álvarez-Rodríguez E., Fernández-Calviño D., Arias-Estévez M. Tetracycline and sulfonamide antibiotics in soils: presence, fate and environmental risks. Processes. 2020; 8(11): 1479. https://doi.org/10.3390/PR8111479
22. Tan H., Kong D., Ma Q., Li Q., Zhou Y., Jiang X. et al. Biodegradation of Tetracycline Antibiotics by the Yeast Strain Cutaneotrichosporon dermatis M503. Microorganisms. 2022; 10(3): 565. https://doi.org/10.3390/microorganisms10030565
Review
For citations:
Antropova N.S., Streletskiy A.V., Ushakova O.V., Yudin S.M. Features of the behavior of the antibiotic tetracycline hydrochloride in the soil environment. Russian Journal of Occupational Health and Industrial Ecology. 2025;65(7):477-483. (In Russ.) https://doi.org/10.31089/1026-9428-2025-65-7-477-483. EDN: lrikcj