Glyphosate concentration and phytotoxicity in Lactuca sativa Buttercrunch
DOI:
https://doi.org/10.5902/2236117062665Keywords:
Agrochemical, Toxicity, N-(phosphonomethyl) glycineAbstract
Agrochemicals, also known as agrotoxics or pesticides, have been widely used to control the proliferation of pests and weeds in agricultural crops to ensure high planting productivity. Among the most used pesticides in the world is the herbicide glyphosate (N-(phosphonomethyl) glycine), because it proves effective for controlling the annual and perennial growth of weeds in agriculture, forestry, urban areas, and domestic gardens. However, the spraying of this compound on a large scale has caused concern, since it accumulates in the topsoil and can generate negative environmental impacts and damage to human health, as it has toxic potential. Given the above, this study evaluated the phytotoxicity of agrochemical solutions glyphosate in different concentrations for the lettuce species Lactuca sativa Buttercrunch, considering number of germinated seeds, stem length, and root length as parameters of analysis. The concentrations of glyphosate tested were 0.001 mg. L-1; 0.1 mg. L-1; 0.5 mg. L-1; 1 mg. L-1 and 20 mg. L-1. The trial followed the procedures described by the United States Environmental Protection Agency. For the statistical analysis, were considered the number of germinated seeds of each treatment and the length of the roots and stem of each of the germinated seeds, which were inserted into equations for the definition of the percentage parameters of Germination Effect (%GE), Root Growth Inhibition (%RGI) and Germination Index (%GI). Analysis of variance (ANOVA) was performed to test for statistically significant differences among the groups and compared by applying the Tukey Test at the level of 5% significance. The results revealed that there was 62.62% RGI and a GI of only 0.37% in treatment with glyphosate solution with concentration of 20 mg. L-1, indicating that high concentrations of the herbicide have toxic effects for the growth of lettuce species Lactuca sativa Buttercrunch. Only the concentration of 20 mg. L-1 obtained a significant difference in relation to the other concentrations evaluated, including the control treatment for the variable "root growth". Thus, for future work it is recommended that glyphosate solutions with concentrations between 1 and 20 mg. L-1 be evaluated and tested for phytotoxicity, cytotoxicity and genotoxicity.
Downloads
References
ABDELHAMEED, R.M.; EL-ZAWAHRY, M.; EMAM, H.E.; 2018. Efficient removal of organophosphorus pesticides from wastewater using polyethylenimine-modified fabrics. Polymer, v. 155, p. 225-234.
AKTAR, W.; SENGUPTA, D.; CHOWDHURY, A; 2009. Impact of pesticides use in agriculture: their benefits and hazards. Interdisciplinary Toxicology, v. 2(1), p. 1–12.
ANNETT, R.; HABIBI, H. R.; HONTELA, A; 2014. Impact of glyphosate and glyphosate-based herbicides on the freshwater environment. Journal of Applied Toxicology, v. 34(5), p. 458–479.
BOOCOCK, M. R.; COGGINS, J. R; 1983. Kinetics of 5-enolpyruvylshikimate-3-phosphate synthase inhibition by glyphosate. FEBS Letters, v. 154(1), p. 127–133.
BRASIL; 2017. Portaria de Consolidação n°5 de 28 de setembro de 2017. Ministério da Saúde, p. 1-926.
DE BRITO RODRIGUES, L.; DE OLIVEIRA, R.; ABE, F.R.; BRITO, L.B.; MOURA, D.S.; Valadares, M.C.; Grisolla, C.K., De Oliveira, D.P.; De Oliveira, G.A.R.; 2017.
Ecotoxicological assessment of glyphosate-based herbicides: Effects on different organisms. Environmental Toxicology and Chemistry, v. 36 (7), p. 1755–1763.
DEBNATH, D.; GUPTA, A. K.; GHOSAL, P. S; 2019. Recent advances in the development of tailored functional materials for the treatment of pesticides in aqueous media: A review. Journal of Industrial and Engineering Chemistry, v. 70, p. 51-69.
DUKE, S. O.; POWLES, S. B; 2008. Glyphosate: a once-in-a-century herbicide. Pest Management Science, v. 64(4), p. 319–325.
FLORENCIA, M.F.; TORRES, C.; BRACAMONTE, E.; GALETTO, L.; 2017. Effects of the herbicide glyphosate on non-target plant native species from Chaco forest (Argentina). Ecotoxicology and Environmental Safety, v. 144, p. 360–368.
GAZOLA, R.P.D.; BUZETTI, S.; GAZOLA, R.N.; DE CASTILHO, R.M.M.; FILHO, M.C.M.T.; CELESTRINO, T.S.; DUPAS, E.; 2016. Nitrogen dose and type of herbicide used for growth regulation on the green coloration intensity of Emerald grass. Ciência Rural, v. 46 (6), p. 984–990.
GÖDE, J. N.; SOUZA, D. H.; TREVISAN, V.; SKORONSKI, E.; 2019. Application of the Fenton and Fenton-like processes in the landfill leachate tertiary treatment. Journal of environmental Chemical Engineering, v. 7, p. 1-8.
GRYCZAK, M.; KILIPPER, J. T.; COSTA, P. D. DE; MACCARI, A.; 2018. Sementes de Lactuca Sativa como bioindicador de toxicidade em resíduos de construção civil. Revista Tecnologia e Ambiente, v. 24, p. 233–242.
KONSTANTINOU, I. K.; HELA, D. G.; ALBANIS, T. A.; 2006. The status of pesticide pollution in surface waters (rivers and lakes) of Greece. Part I. Review on occurrence and levels. Environmental Pollution, v. 141(3), p. 555–570.
MAGDALENO, A.; PERALTA GAVENSKY, M.; FASSIANO, A. V.; RÍOS DE MOLINA, M. C.; SANTOS, M.; MARCH, H.; MORETTON, J.; JUÁREZ, Á. B.; 2015. Phytotoxicity and genotoxicity assessment of imazethapyr herbicide using a battery of bioassays. Environmental Science and Pollution Research, v. 22(23), p. 19194–19202.
MAURYA, P.; YADAV, L.; 2014. Uses of pesticide in foods : Curse for health. Asian Journal of Bio Science, v. 9(1), p. 123–128.
MDH; 2017. Glyphosate and Drinking Water. Minnesota Department of Health, October, p.1-2.
MEFTAUL, I.M.; VENKATESWARLU, K.; DHARMARAJAN, R.; ANNAMALAI, P.; ASADUZZAMAN, M.; PARVEN, A.; MEGHARAJ, M.; 2020. Controversies over human health and ecological impacts of glyphosate: Is it to be banned in modern agriculture? Environmental Pollution, v. 263, p. 114372.
MESNAGE, R.; DEFARGE, N.; SPIROUX DE VENDÔMOIS, J.; SÉRALINI, G. E.; 2015. Potential toxic effects of glyphosate and its commercial formulations below regulatory limits. Food and Chemical Toxicology, v. 84, p. 133–153.
MORAES, R.F.DE.; 2019. Agrotóxicos no Brasil: padrões de uso, política da regulação e prevenção da captura regulatória. Instituto de Pesquisa Econômica Aplicada, p. 84.
PFLEEGER, T.; BLAKELEY-SMITH, M.; KING, G.; LEE, E.H.; PLOCHER, M.; OLSZYK, D.; 2012. The effects of glyphosate and aminopyralid on a multi-species plant field trial. Ecotoxicology, v. 21 (7), p. 1771–1787.
QI, H.; HUANG, Q.; HUNG, Y.-C.; 2018. Effectiveness of electrolyzed oxidizing water treatment in removing pesticide residues and its effect on produce quality. Food Chemistry, Elsevier Ltd, v. 239, p. 561–568.
ROSE, T.J.; ZWIETEN, L.V.; CLAASSENS, A.; SCANLAN, C.; ROSE, M.T.; 2018. Phytotoxicity of soilborne glyphosate residues is influenced by the method of phosphorus fertiliser application. Plant and Soil, v. 422 (1–2), p. 455–465.
SIKORSKI, L.; BACIAK, M.; BES, A.; ADOMAS, B.; 2019. The effects of glyphosate-based herbicide formulations on Lemna minor, a non-target species. Aquatic Toxicology, v. 209, p. 70–80.
USEPA; 1996. Ecological effects test guidelines earthworm subchronic toxicity Test. United States Environmental Protection Agency, April, p. 1–11.
WANG, S.; SEIWERT, B.; KÄSTNER, M.; MILTNER, A.; SCHÄFFER, A.; REEMTSMA, T.; YANG, Q.; NOWAK, K. M.; 2016. (Bio)degradation of glyphosate in water-sediment microcosms – A stable isotope co-labeling approach. Water Research, v. 99, p. 91–100.
ZHAN, H.; FENG, Y.; FAN, X.; CHEN, S.; 2018. Recent advances in glyphosate biodegradation. Applied Microbiology and Biotechnology, v. 102(12), p. 5033–5043.
ZHANG, J.-W.; XU, D.-Q.; FENG, X.-Z.; 2019. The toxic effects and possible mechanisms of glyphosate on mouse oocytes. Chemosphere, Elsevier Ltd, v. 237, p. 1-10.
Published
Versions
- 2022-07-28 (2)
- 2020-12-04 (1)
How to Cite
Issue
Section
License
Copyright (c) 2020 Revista Eletrônica em Gestão, Educação e Tecnologia Ambiental
This work is licensed under a Creative Commons Attribution-NonCommercial-ShareAlike 4.0 International License.
DECLARATION