Abstract:Adjuvants, such as mineral oils, are widely used in the application of herbicides by reducing the drift and evaporation of the droplets and by increasing herbicide uptake by the plant. However, little is known about how mineral oil behaves when in contact with the soil. Thus, the objective of this research was to evaluate the transport of atrazine via leaching with the addition of mineral oil in a soil agricultural under laboratory conditions. To quantify the concentration of the herbicide along the profile of… Show more
“…On the other hand, adjuvants such as mineral oils are widely used in herbicide application to reduce drift and droplet evaporation, as well as to enhance herbicide absorption by the plant. Thus, the addition of mineral oil (1 and 2% v/v) at the time of pre-emergence atrazine application did not interfere with the transport of this herbicide in the arable soil profile via leaching; therefore, the adjuvant may have a positive effect only on the herbicide-plant relationship [68].…”
Herbicides play a crucial role in weed control in various agricultural and non-agricultural settings. However, their behavior in the environment is complex and influenced by multiple factors. Understanding their fate and retention, transport, and transformation is essential for effective herbicide management and minimizing their impact on ecosystems. This chapter begins by emphasizing the importance of studying herbicide behavior in real-world conditions, considering physical, chemical, and biological amendments in soil. It highlights how these amendments can directly affect weed control efficacy when residual herbicides are applied in pre-emergence. Detailed knowledge of herbicide behavior in the environment enables the adjustment of application rates based on soil type and climatic conditions, which is a key aspect of precision agriculture. The study of herbicide interactions in the environment has experienced significant growth across various subfields, particularly in the last three decades. It can be considered a multidisciplinary subject that encompasses areas such as agricultural, environmental, and biological sciences, as well as technology, physics, chemistry, and biomedicine. Overall, there are over 35,000 papers on herbicide behavior in the environment, and the trend indicates that the number of publications will continue to grow in the coming years.
“…On the other hand, adjuvants such as mineral oils are widely used in herbicide application to reduce drift and droplet evaporation, as well as to enhance herbicide absorption by the plant. Thus, the addition of mineral oil (1 and 2% v/v) at the time of pre-emergence atrazine application did not interfere with the transport of this herbicide in the arable soil profile via leaching; therefore, the adjuvant may have a positive effect only on the herbicide-plant relationship [68].…”
Herbicides play a crucial role in weed control in various agricultural and non-agricultural settings. However, their behavior in the environment is complex and influenced by multiple factors. Understanding their fate and retention, transport, and transformation is essential for effective herbicide management and minimizing their impact on ecosystems. This chapter begins by emphasizing the importance of studying herbicide behavior in real-world conditions, considering physical, chemical, and biological amendments in soil. It highlights how these amendments can directly affect weed control efficacy when residual herbicides are applied in pre-emergence. Detailed knowledge of herbicide behavior in the environment enables the adjustment of application rates based on soil type and climatic conditions, which is a key aspect of precision agriculture. The study of herbicide interactions in the environment has experienced significant growth across various subfields, particularly in the last three decades. It can be considered a multidisciplinary subject that encompasses areas such as agricultural, environmental, and biological sciences, as well as technology, physics, chemistry, and biomedicine. Overall, there are over 35,000 papers on herbicide behavior in the environment, and the trend indicates that the number of publications will continue to grow in the coming years.
“…A atrazine e [atrazine + simazine] demonstraram redução de controle a partir dos 30 DAT, o que pode ser atribuído a perda de residual do herbicida no solo (Tabela 2). Esse fato pode decorrer pelo processo de lixiviação, uma vez que as unidades experimentais receberam irrigação constante e, o grupo das triazinas apresenta alto potencial de perdas por lixiviação (Mendes et al, 2019). O tratamento com metribuzin atingiu valores de controle acima dos 80% até 21 DAT, nas demais avaliações apresentou perdas drásticas de controle, chegando aos 60 DAT com resultado somente superior a testemunha sem herbicida.…”
“…The downward movement of herbicides in the soil or along the soil water is called leaching or percolation (Mancuso et al, 2011;Franceschi et al, 2019;Mendes et al, 2019). It is known, for instance, that the leaching potential of herbicides such as the S-metolachlor can be influenced by natural precipitation and/or artificial irrigation or by soils that have large pores or are poor in organic matter.…”
Information about the impact of herbicides in the soil based on the growth of bioindicator species is extremely useful in developing crop management strategies. Therefore, this study aims to evaluate the leaching potential of the herbicide S-metolachlor under different natural precipitations in medium-textured Oxisol using bioindicator plants. A completely randomized experimental design was adopted, with four replicates and treatments arranged in a 3 × 8 factorial scheme [three indexes of precipitation occurred in the environment before the collection of the samples (50, 91, and 131 mm) and eight depths in the soil profile (0-0.03; 0.03-0.06; 0.06-0.09; 0.09-0.12; 0.12-0.15; 0.15-0.20; 0.20-0.25; 0.25-0.30 m)]. PVC columns were used, maintaining the original soil integrity during sampling after accumulating the stipulated natural precipitation. Longitudinal sections separated the columns to sow the bioindicator species (cucumber, lettuce, Alexander grass, and sorghum). The phytotoxicity symptoms of bioindicator plants were evaluated, adopting a phytotoxicity visual scale between 0 and 100%, at 5, 7, 9, and 11 days after seeding. The responses of the bioindicator species to the residual effect of the herbicide S-metolachlor were variable and depended on the rainfall level. Generally, in a medium-textured Oxisol, the higher values of concentration of S-metolachlor occurs in depths ranging between 0 and 0.06 m. The maximum leaching depth detected was 0.12-0.15 m with 131 mm of precipitation. Cucumber was the most sensitive species to the presence of S-metolachlor in an Oxisol of medium-texture since it presents symptoms of phytotoxicity at higher depths.
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