Toxicology Clinical Trial
— VESTALOfficial title:
Temporal Variation of the Exposure to Pesticides in the Employees of the Limoges University Hospital
In a sample of 300 employees of the Limoges University Hospital, it is proposed to explore the intraindividual and interindividual variability of urinary concentrations of glyphosate and 320 other pesticides. The employees will fill a questionary in which will allow to explore the relationships between the concentrations, lifestyle and dietary habits.
Status | Recruiting |
Enrollment | 300 |
Est. completion date | October 23, 2024 |
Est. primary completion date | October 17, 2024 |
Accepts healthy volunteers | Accepts Healthy Volunteers |
Gender | All |
Age group | 18 Years and older |
Eligibility | Inclusion Criteria: - Adult 18 years and over. - Employed by the University Hospital of Limoges. - Having consented to participate in the study after being informed. Exclusion Criteria: - Adult with a professional activity during which he is required to handle or come into contact with glyphosate |
Country | Name | City | State |
---|---|---|---|
France | CHU de Limoges | Limoges |
Lead Sponsor | Collaborator |
---|---|
University Hospital, Limoges |
France,
Type | Measure | Description | Time frame | Safety issue |
---|---|---|---|---|
Primary | glyphosate overconsumption | Proportion of individuals with an estimated daily consumption of glyphosate greater than the acceptable daily intake of glyphosate | 1 week | |
Secondary | Identification of determinant of exposure to glyphosate | Proportion of individuals with a daily consumption of glyphosate greater than the acceptable daily intake according to socio-demographic determinants(age, sex, profession and socio-professional category) | 1 week | |
Secondary | Identification of determinant of exposure to glyphosate | Proportion of individuals with a daily consumption of glyphosate greater than the acceptable daily intake according to lifestyles (city center, peri-urban, rural ) | 1 week | |
Secondary | Identification of determinant of exposure to glyphosate | Proportion of individuals with a daily consumption of glyphosate greater than the acceptable daily intake according to proximity to agricultural activities | 1 week | |
Secondary | Identification of determinant of exposure to glyphosate | Proportion of individuals with a daily consumption of glyphosate greater than the acceptable daily intake according to use of glyphosate at home | 1 week | |
Secondary | Identification of determinant of exposure to glyphosate | Proportion of individuals with a daily consumption of glyphosate greater than the acceptable daily intake according to dietary habits | 1 week | |
Secondary | Coefficient of variation of the glyphosate concentrations | Calculation of the coefficient of variation of the glyphosate concentrations measured 3 times over a period of 24 hours | 1 week | |
Secondary | Intra-individual variability of urinary glyphosate concentrations | Comparison of the average GLP concentrations measured on 3 occasions (at sunrise, in the middle then at the end of the day) over a period of 24 hours. | 1 week | |
Secondary | Impact of urine sample collection schedule on glyphosate concentration measurement | According to the methodology proposed by Wang et al. : a linear mixed-effects model to determine which measure produces the best estimate of exposure; itself obtained by calculating the mean of the observed values. | 1 week | |
Secondary | Identification of determinants of exposure to a panel of around 320 pesticides | Proportion of subjects with a detectable concentration among the 320 pesticides measured by specific LC-MS and GC-MS methods and prevalence of individuals with a detectable concentration according to socio-demographic determinants | 1 week | |
Secondary | Identification of determinants of exposure to a panel of around 320 pesticides | Proportion of subjects with a detectable concentration among the 320 pesticides measured by specific LC-MS and GC-MS methods and prevalence of individuals with a detectable concentration according to lifestyles | 1 week | |
Secondary | Identification of determinants of exposure to a panel of around 320 pesticides | Proportion of subjects with a detectable concentration among the 320 pesticides measured by specific LC-MS and GC-MS methods and prevalence of individuals with a detectable concentration according to proximity to agricultural activities | 1 week | |
Secondary | Identification of determinants of exposure to a panel of around 320 pesticides | Proportion of subjects with a detectable concentration among the 320 pesticides measured by specific LC-MS and GC-MS methods and prevalence of individuals with a detectable concentration according to use of glyphosate at home | 1 week | |
Secondary | Identification of determinants of exposure to a panel of around 320 pesticides | Proportion of subjects with a detectable concentration among the 320 pesticides measured by specific LC-MS and GC-MS methods and prevalence of individuals with a detectable concentration according to dietary habits | 1 week | |
Secondary | Intra-individual variability of urinary 320 pesticides concentrations | Calculation of the coefficient of variation of the concentrations of each of the pesticides (expressed in µg/L or µg/g of creatinine) measured 3 times (at sunrise, in the middle and then at the end of the day) over a period of 24 hours | 1 week | |
Secondary | Impact of urine sample collection schedule on 320 pesticides concentration measurement | Comparison of the average concentrations of each of the pesticides measured on 3 occasions (at sunrise, in the middle and then at the end of the day) over a period of 24 hours. According to the methodology proposed by Wang et al.: a linear mixed-effects model to determine which measure produces the best estimate of exposure; itself obtained by calculating the mean of the observed values. | 1 week |
Status | Clinical Trial | Phase | |
---|---|---|---|
Not yet recruiting |
NCT02775890 -
Potential Lead Exposure Through Eating Self-harvested Wild Game
|
N/A |