2021
DOI: 10.1016/j.envres.2021.110871
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The role of two organic amendments to modify the environmental fate of S-metolachlor in agricultural soils

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Cited by 31 publications
(8 citation statements)
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“…Moreover, a negative correlation between DT 50 values of s-metolachlor with soil organic carbon content has been reported in the literature [ 79 , 80 ]. Corroborating these findings, a recent study by Marín-Benito, et al [ 81 ] reported slower dissipation and leaching of s-metolachlor in soils amended with green compost and pelletized manure compared to unamended soils. DT 50 values of metolachlor were prolonged from 37.9 to 126 days to 49.5 to 135.9 days for two different soil types under soil sterilization in China, indicating that microbial degradation was the dominant pathway for metolachlor and s-metolachlor degradation in soils [ 80 , 82 ].…”
Section: Environmental Fate Of Herbicides Utilized In Tomato Productionmentioning
confidence: 67%
“…Moreover, a negative correlation between DT 50 values of s-metolachlor with soil organic carbon content has been reported in the literature [ 79 , 80 ]. Corroborating these findings, a recent study by Marín-Benito, et al [ 81 ] reported slower dissipation and leaching of s-metolachlor in soils amended with green compost and pelletized manure compared to unamended soils. DT 50 values of metolachlor were prolonged from 37.9 to 126 days to 49.5 to 135.9 days for two different soil types under soil sterilization in China, indicating that microbial degradation was the dominant pathway for metolachlor and s-metolachlor degradation in soils [ 80 , 82 ].…”
Section: Environmental Fate Of Herbicides Utilized In Tomato Productionmentioning
confidence: 67%
“…These previous studies targeted metabolites of S -metolachlor that could be produced in the plant seedling within a short time of 24 h after herbicide exposure, and thus magnitudes of MOC-OA and -ESA produced for 24 h might be below their detectable limits. MOC-OA and -ESA are the main metabolites of S -metolachlor that can be produced primarily by microbial activity in ground and surface water and soil. In this study, MOC-ESA was not detected from rinsates of tested Petri dish and seed/seedling surfaces, but residues of MOC-OA (86–260 ng) were detected in the rinsates (Norsworthy, unpublished data). Although residual trends of MOC-OA in the rinsates did not show differences between treatments with S and R biotypes, there was a potential that some residues of MOC-OA produced outside seeds/seedlings could be absorbed into the plant samples during the study.…”
Section: Resultsmentioning
confidence: 99%
“…The highest increase was observed for three-component heterostructure which reach 61.08% photocatalytic turnover rate, after 8 h of irradiation. These results are significant considering that S-MCh is considered to be a reluctant molecule towards photocatalytic decomposition due to the structural stability induced by the aromatic cycle and functional groups [ 39 , 40 ]. The formation of bi-products with pollutant potential cannot be excluded as partial oxidation may induce the development of carboxylic acids.…”
Section: Resultsmentioning
confidence: 99%