2019
DOI: 10.1016/j.jhazmat.2019.04.075
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Dynamic modeling of famoxadone and oxathiapiprolin residue on cucumber and Chinese cabbage based on tomato and lettuce archetypes

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Cited by 29 publications
(22 citation statements)
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“…Yu et al used UPLC-MS/MS to study the dissipation of oxathiapiprolin in grapes and soil, the half-lives of oxathiapiprolin in grapes and soil were reported at 8.6-9.2 days and 7.6-12.0 days, respectively, whereas the terminal residues in grape were 0.002(LOQ)-0.022 mg/kg after 14 days [20]. Feng et al analyzed the uptake and distribution of oxathiapiprolin, IN-WR791 and IN-E8S72 residues in tomatoes, cucumbers, lettuce, and Chinese cabbage to test the viability of applying the dynamic plant uptake model (dynamiCROP) in modeling pesticide residues in other crops [21,22]. Wang et al established a modified QuECh-ERS purification scheme, and used LC-MS/MS detection for oxathiapiprolin, IN-SXS67 and IN-E8S72 residues in cucumbers; recovery rates ranged from 77.4 to 111.3%, RSDs were 1.0−8.5%, and LOQs were 0.02 mg/kg, and the dissipation half-lives for oxathiapiprolin in cucumbers ranged from 2.4 to 4.0 days [23].…”
Section: Introductionmentioning
confidence: 99%
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“…Yu et al used UPLC-MS/MS to study the dissipation of oxathiapiprolin in grapes and soil, the half-lives of oxathiapiprolin in grapes and soil were reported at 8.6-9.2 days and 7.6-12.0 days, respectively, whereas the terminal residues in grape were 0.002(LOQ)-0.022 mg/kg after 14 days [20]. Feng et al analyzed the uptake and distribution of oxathiapiprolin, IN-WR791 and IN-E8S72 residues in tomatoes, cucumbers, lettuce, and Chinese cabbage to test the viability of applying the dynamic plant uptake model (dynamiCROP) in modeling pesticide residues in other crops [21,22]. Wang et al established a modified QuECh-ERS purification scheme, and used LC-MS/MS detection for oxathiapiprolin, IN-SXS67 and IN-E8S72 residues in cucumbers; recovery rates ranged from 77.4 to 111.3%, RSDs were 1.0−8.5%, and LOQs were 0.02 mg/kg, and the dissipation half-lives for oxathiapiprolin in cucumbers ranged from 2.4 to 4.0 days [23].…”
Section: Introductionmentioning
confidence: 99%
“…Feng et al. analyzed the uptake and distribution of oxathiapiprolin, IN‐WR791 and IN‐E8S72 residues in tomatoes, cucumbers, lettuce, and Chinese cabbage to test the viability of applying the dynamic plant uptake model (dynamiCROP) in modeling pesticide residues in other crops [21,22]. Wang et al.…”
Section: Introductionmentioning
confidence: 99%
“…39 Together, these models have guided good agricultural practices, including pesticide application methods and PHI, and improved our understanding of the fate of pesticides in different agricultural environments. However, recent studies on agrochemical concentrations and their fate in the environment have focused mainly on crops, 33,40,41 with less attention being given to the orchard environment.…”
Section: Introductionmentioning
confidence: 99%
“…mineralization, soil sorption), which in turn also controls the leaching of chemicals Jacobsen et al, 2015). Researchers have developed different models for predicting the environmental fate of agricultural pesticides in food crops and plant components using different physico-chemical parameters such as degradation, phase partitioning, and intermedia transport (Kumari et al, 2022;Feng et al, 2019;Wani et al, 2019;Fantke and Jolliet, 2016). The limitations (long field trials and crop-growth periods) of DT 50 determination from lab studies have motivated researchers to discuss consumer risk assessment based on residue and half-life (HL) data using a variety of crop uptake models (Fantke et al, 2011a;Feng et al, 2019;Juraske et al, 2012).…”
mentioning
confidence: 99%
“…Researchers have developed different models for predicting the environmental fate of agricultural pesticides in food crops and plant components using different physico-chemical parameters such as degradation, phase partitioning, and intermedia transport (Kumari et al, 2022;Feng et al, 2019;Wani et al, 2019;Fantke and Jolliet, 2016). The limitations (long field trials and crop-growth periods) of DT 50 determination from lab studies have motivated researchers to discuss consumer risk assessment based on residue and half-life (HL) data using a variety of crop uptake models (Fantke et al, 2011a;Feng et al, 2019;Juraske et al, 2012). These models simulate pesticide distribution in particular crops and are used to calculate pesticides intake and related health risks for the interpretation of the consumption residues of pesticides/or their behavior in the crops and environment (e.g.…”
mentioning
confidence: 99%