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Monitoring the Persistence of Devrinol, Diazinon, and Trifluralin Residues in Soil Following Application of Organic Amendments

Received: 23 February 2022    Accepted: 18 March 2022    Published: 10 May 2022
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Abstract

Pesticides have the potential mobility from the site of application to natural water resources leading to surface water quality problems. Binding pesticides to soil lead to immobilization preventing their mobility into surface water and enhancing their availability for degradation by soil microorganisms and their secreting enzymes. The impact of low-cost organic amendments used in agricultural operations on the persistence of three pesticides; devrinol, diazinon, and trifluralin in agricultural soil was investigated. Pesticide residues in sewage sludge (SS), farm compost (Comp), and no-mulch (NM) control treatment following field application were monitored at different time intervals using solvent partitioning and gas chromatographic procedure (GC). Half-life (T1/2) values of the three pesticides in soil were determined under three farming practices to investigate how long each pesticide remains in each soil treatment. Results revealed the retention of devrinol by 30%, diazinon by 55%, and trifluralin by 80% in soil amended with SS compared to sole NM soil used as control treatment. This practice might prevent the off-site movement of pesticides. Devrinol T1/2 value of 14.1 days was significantly (P≤ 0.05) lower in soil amended with Comp compared to SS amended soil due to its high dissipation constant (K). Diazinon residues fluctuated during the first week after spraying and started to decline, reaching a minimum value of 0.004 µg g-1 soil at 35 days after spraying. Its T1/2 value of 10.6 days was significantly lower in SS amended soil compared to Comp waste and control treatments (15.8 and 18.5 days, respectively). Trifluralin residues in NM soil showed a low dissipation constant and greater (T1/2) value of 116 days. Its dissipation and degradation in soil amended with Comp and SS indicated half-life (T1/2) values of 48.5 and 34.6 days, respectively. The low adsorptive capacity of devrinol due to its high-water solubility requires minimizing its application rates in agricultural regions to prevent environmental contamination of natural water resources.

Published in International Journal of Applied Agricultural Sciences (Volume 8, Issue 3)
DOI 10.11648/j.ijaas.20220803.11
Page(s) 104-112
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This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2024. Published by Science Publishing Group

Keywords

Pesticide Binding, Gas Chromatography, Dissipation Constants, Half-Lives, Initial Residues

References
[1] U.S. Environmental Protection Agency (US EPA). Pesticide sales and usage report, 2004. EPA-733-R-04-001, Washington, D. C., USA.
[2] U.S. Environmental Protection Agency (US EPA), Washington, D. C., 2004. National Summary of Impaired Waters and TMDL Information. Available at http://iaspub.epa.gov/tmdlwaters10/attainsnationcy.control?preporttype=T
[3] Antonious, G. F. (2000). Clomazone residues in soil and runoff: Measurement and mitigation. Bull. Environ. Contam. Toxicol. 64 (2), 168-175.
[4] Antonious, G. F., Turley, T., Hill, R. (2014). Impact of soil amendments on metribuzin and DCPA half-lives and mobility into agricultural runoff water. J. Environmental Science and Health, Part B 49, 313–323.
[5] Antonious, G. F., Patterson, M. A. (2005). Napropamide residues in runoff and infiltration water from pepper production. J. Environ. Sci. Health, B40 (3), 385-396.
[6] Antonious, G. F. (2018). Impact of Animal Manure on Phytochemicals in Hot Pepper Fruits. Chapter 1, In: Solanaceae: Cultivation, Nutrition and Health. Edited by Rocka, IS, Plant Science Health and Practices, pages 1-42. Nova Science Publishers, New York, USA.
[7] Antonious, G. F. (2016). Soil amendments for agricultural production. Chapter 7 In: Organic Fertilizers: From Basic Concepts to Applied Outcomes, Book chapter, July 2016, pages 157-187. Edited by Larramendy ML & Soloneski S, Published by Intech, Janeza Trdine 9, 51000 Rijeka, Croatia.
[8] Antonious, G. F., Turley, E. T., Nkuwi, L. (2016). Impact of soil amendments and biochar on yield of tomato grown under field conditions. Fruit and Vegetable Research Report, 2016 Annual Research Report, University of Kentucky, College of Agriculture, Food and Environment, PR-721, pp. 25-26.
[9] Antonious, G. F., Turley, E. T., and Dawood, M. (2020). Monitoring soil enzymes activity before and after animal manure application. J. of Agriculture, 10, 166.
[10] Antonious, G. F., Turley, E. T., Shrestha D. S., and Dawood, M. H. (2021). Variability of biochar performance among soil amendments and enzymes activity. International Journal of Applied Agricultural Sciences (IJAAS), 7 (1), 66-76.
[11] Antonious, G. F., Dawood, M. H., Turley, E. T., and Paxton, R. B. (2021). Yield and quality of lettuce, pumpkin, and watermelon varieties grown under five soil management practices. International Journal of Applied Agricultural Sciences (IJAAS), 7 (1), 57-65.
[12] Antonious, G. F., Dawood, M. H., Turley, E. T., and Paxton, R. B. (2022). Biochar and animal manures increased yield of three varieties of turnips. International Journal of Applied Agricultural Sciences (IJAAS), 8 (1), 50-56.
[13] Antonious, G. F. (2009). Enzyme activities and heavy metals concentration in soil amended with sewage sludge. J. Environ. Science & Health, Part-A Toxic/Hazardous Substances and Environmental Engineering, A44, 1019-1024.
[14] Antonious, G, F. (2003). Impact of soil management and two botanical insecticides on urease and invertase activity. J. Environ. Sci. Health, B38 (4), 479-488.
[15] Cox L, Cecchi A, Celis R, Hermos´ın M, Koskinen W, Cornejo J. (2001). Effect of exogenous carbon on movement of simazine and 2,4-D in soils, Soil Sci. Soc. Am. J. 65, 1688–1695.
[16] Antonious, G. F., Turley, E. T., Snyder, J, C. (2008). Soil enzyme activity and heavy metal contamination in soil amended with sewage sludge. A paper presented at the International Symposium on Environment, Athens, Greece, May 22-25, 2008. Book chapter, In Environmental Engineering & Economics, by Michael Theophanides, Institute for Education and Research.
[17] Barriuso, E., Houot. S., Serra-Wittling, C. (1997). Influence of compost addition to soil on the behavior of herbicides. Pestic. Sci. 49, 65-75.
[18] Stratton ML, Rechcigl JE. Organic mulches, wood products, In: Handbook of Soil Conditioners. Wallace A.; Terry R. Eds. Marcel Dekker, Inc., New York, 1998, 43-95.
[19] Colovic, M., Krstic, D., Petrovic, S., Leskovac, A., Joksie, A., Franko, M., Trebse, P., Vasic, V. (2010). Toxic effects of diazinon and its photodegradation products. Toxicol. Lett. 193, 9-18.
[20] Coolong T, Bessin R, Jones T, Strang J, Seebold K. Vegetable Production Guide for Commercial Growers, Cooperative Extension Service Bulletin ID-36, University of Kentucky, College of Agriculture, 2011, Lexington, KY.
[21] Aguer, J. P., Cox, L., Richard, C., Hermosin, M. C. and Cornejo, J. (2000). Sorption and photolysis studies in soil and sediment of the herbicide napropamide. Journal of Environmental Science & Health Part B, 35 (6), pp. 725-738.
[22] SAS Institute Inc. SAS/STAT Guide, Version 6.4 SAS 2016 Inc., Campus Drive, Cary, NC 27513.
[23] Biswas, P. K., Pramanik S. K., Mitra S. R., Bhattacharyya A. (2007). Persistence of napropamide in/ on tea under North-East Indian climatic condition. Bull. Environ. Contam. Toxicol. 79 (5), 566–569.
[24] Donaldson S. G., Miller G. C. 1996. Coupled transport and photodegradation of napropamide in soils undergoing evaporation from a shallow water table. Environ. Sci. Technol. 30 (2), 924–930.
[25] Tomlin, CDS. The pesticide Manual, 15th Edition published by the British Crop Production Council, 2009 British Library Cataloguing Publication Data (BCPC), Published by the Royal Society of Chemistry.
[26] Messersmith C. G., Burnside, O. C. and Lavy T. L. (1971.) Biological and non-biological dissipation of trifluralin from soil. Weed Sci., 19, 285-290.
[27] Sparks, D. L. Chemistry of soil organic matter. In: International Soil Chemistry; Academic Press, San Diego, CA, 1995, 53-79.
[28] Pierce, R. H. Olney, C. E., Felbeck, G. T. (1971). Pesticide adsorption in soils and sediments. Environ. Lett. 1 (2), 157-172.
[29] Senesi, N., Testini, C., (1980). Adsorption of some nitrogenated herbicides by soil humic acids. Soil Science 10, 314-320.
[30] Senesi, N., Testini, C. (1983). The environmental fate of herbicides: The role of humic substances. Ecology Bulletin 35, 477-490.
[31] Dzombak, D. A., and F. M. M. Morel. (1990). Surface complexation modeling: hydrous ferric oxide. New York: Wiley and Sons.
[32] Stumm, W. (1992). Chemistry of the solid-water interface. New York: Wiley and Sons. M. Colovic, D., Krastic, S., Petrovie, A., Leaskovac, G., Joksic, J., Savic, M., Franko, P., Trebse, V. Vasic. Toxic effects of diazinon and its photodegradation products. Toxicol Lett, 193, 9-18.
[33] Horowitz, M., Nirahulin, T. Blumenfeld, T. (1974). Behaviour and persistence of trifluralin in soil., 14 (4), 213–220.
[34] Messersmith, C. G., Burnside, O. C., Lavy, T. L. (1971). Biological and Non-Biological Dissipation of Trifluralin from Soil. Weed Science Society of America, 1971, pp. 285–90,
[35] Bardsley, C. E., Savage K. E., Childers V. O. (1967) Trifluralin behavior in soil. I. Toxicity and persistence as related to organic matter, Agron. 59, 159-160.
[36] Gilliom, R. J, Barbash, J. E., Kolpin, D. W., Larson, S. J. (1999). Testing water quality for pesticide pollution. Environ. Sci. Technol. 33, 164A-169A.
[37] Kizilkaya, R,, Bayrakli, B. (2005). Effect of N-enriched sewage sludge on soil enzyme activities. Appl. Soil Ecol. 30, 192–202.
[38] Cotrufo, M. F., Ineson, P., Roberts, J. D. (1995). Decomposition of birch leaf litters with varying C-to-N ratios. Soil Biol. Biochem. 27, 1219–1221.
[39] Recous, S., Robin, D., Darwis, D,, Mary, B.(1995). Soil inorganic N availability: Effect on maize residue decomposition. Soil Biol. Biochem. 27, 1529–1538.
[40] Vargas, D. N., Bertiller, M. B., Ares, J. O., Carrer, A. L., Sain, C. L. (2006). Soil C and N dynamics induced by leaf-litter decomposition of shrubs and perennial grasses in the Patagonian Monte. Soil Biol. Biochem. 38, 2401–2410.
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    George Fouad Antonious. (2022). Monitoring the Persistence of Devrinol, Diazinon, and Trifluralin Residues in Soil Following Application of Organic Amendments. International Journal of Applied Agricultural Sciences, 8(3), 104-112. https://doi.org/10.11648/j.ijaas.20220803.11

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    George Fouad Antonious. Monitoring the Persistence of Devrinol, Diazinon, and Trifluralin Residues in Soil Following Application of Organic Amendments. Int. J. Appl. Agric. Sci. 2022, 8(3), 104-112. doi: 10.11648/j.ijaas.20220803.11

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    AMA Style

    George Fouad Antonious. Monitoring the Persistence of Devrinol, Diazinon, and Trifluralin Residues in Soil Following Application of Organic Amendments. Int J Appl Agric Sci. 2022;8(3):104-112. doi: 10.11648/j.ijaas.20220803.11

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  • @article{10.11648/j.ijaas.20220803.11,
      author = {George Fouad Antonious},
      title = {Monitoring the Persistence of Devrinol, Diazinon, and Trifluralin Residues in Soil Following Application of Organic Amendments},
      journal = {International Journal of Applied Agricultural Sciences},
      volume = {8},
      number = {3},
      pages = {104-112},
      doi = {10.11648/j.ijaas.20220803.11},
      url = {https://doi.org/10.11648/j.ijaas.20220803.11},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ijaas.20220803.11},
      abstract = {Pesticides have the potential mobility from the site of application to natural water resources leading to surface water quality problems. Binding pesticides to soil lead to immobilization preventing their mobility into surface water and enhancing their availability for degradation by soil microorganisms and their secreting enzymes. The impact of low-cost organic amendments used in agricultural operations on the persistence of three pesticides; devrinol, diazinon, and trifluralin in agricultural soil was investigated. Pesticide residues in sewage sludge (SS), farm compost (Comp), and no-mulch (NM) control treatment following field application were monitored at different time intervals using solvent partitioning and gas chromatographic procedure (GC). Half-life (T1/2) values of the three pesticides in soil were determined under three farming practices to investigate how long each pesticide remains in each soil treatment. Results revealed the retention of devrinol by 30%, diazinon by 55%, and trifluralin by 80% in soil amended with SS compared to sole NM soil used as control treatment. This practice might prevent the off-site movement of pesticides. Devrinol T1/2 value of 14.1 days was significantly (P≤ 0.05) lower in soil amended with Comp compared to SS amended soil due to its high dissipation constant (K). Diazinon residues fluctuated during the first week after spraying and started to decline, reaching a minimum value of 0.004 µg g-1 soil at 35 days after spraying. Its T1/2 value of 10.6 days was significantly lower in SS amended soil compared to Comp waste and control treatments (15.8 and 18.5 days, respectively). Trifluralin residues in NM soil showed a low dissipation constant and greater (T1/2) value of 116 days. Its dissipation and degradation in soil amended with Comp and SS indicated half-life (T1/2) values of 48.5 and 34.6 days, respectively. The low adsorptive capacity of devrinol due to its high-water solubility requires minimizing its application rates in agricultural regions to prevent environmental contamination of natural water resources.},
     year = {2022}
    }
    

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  • TY  - JOUR
    T1  - Monitoring the Persistence of Devrinol, Diazinon, and Trifluralin Residues in Soil Following Application of Organic Amendments
    AU  - George Fouad Antonious
    Y1  - 2022/05/10
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    JF  - International Journal of Applied Agricultural Sciences
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    AB  - Pesticides have the potential mobility from the site of application to natural water resources leading to surface water quality problems. Binding pesticides to soil lead to immobilization preventing their mobility into surface water and enhancing their availability for degradation by soil microorganisms and their secreting enzymes. The impact of low-cost organic amendments used in agricultural operations on the persistence of three pesticides; devrinol, diazinon, and trifluralin in agricultural soil was investigated. Pesticide residues in sewage sludge (SS), farm compost (Comp), and no-mulch (NM) control treatment following field application were monitored at different time intervals using solvent partitioning and gas chromatographic procedure (GC). Half-life (T1/2) values of the three pesticides in soil were determined under three farming practices to investigate how long each pesticide remains in each soil treatment. Results revealed the retention of devrinol by 30%, diazinon by 55%, and trifluralin by 80% in soil amended with SS compared to sole NM soil used as control treatment. This practice might prevent the off-site movement of pesticides. Devrinol T1/2 value of 14.1 days was significantly (P≤ 0.05) lower in soil amended with Comp compared to SS amended soil due to its high dissipation constant (K). Diazinon residues fluctuated during the first week after spraying and started to decline, reaching a minimum value of 0.004 µg g-1 soil at 35 days after spraying. Its T1/2 value of 10.6 days was significantly lower in SS amended soil compared to Comp waste and control treatments (15.8 and 18.5 days, respectively). Trifluralin residues in NM soil showed a low dissipation constant and greater (T1/2) value of 116 days. Its dissipation and degradation in soil amended with Comp and SS indicated half-life (T1/2) values of 48.5 and 34.6 days, respectively. The low adsorptive capacity of devrinol due to its high-water solubility requires minimizing its application rates in agricultural regions to prevent environmental contamination of natural water resources.
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Author Information
  • Division of Environmental Studies, College of Agriculture, Community and the Sciences, Kentucky State University, Frankfort, USA

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