The Dynamics of Exposure, Phthalates and Asthma in a Randomized Trial (DEPART)
The Dynamics of Exposure, Phthalates, and Asthma project (DEPART) utilizes data and samples collected within the Home Air in Agriculture Pediatric Intervention Trial (HAPI, NIEHS R01 ES023510). The participants are 70 Latino children with asthma aged 6-12 years who reside in rural, agricultural central WA State. They were recruited from 2015-2017 for a one-year follow up period of their asthma morbidity following randomization into a control group (education) or intervention (education plus 2 in home portable HEPA air cleaners). Follow assessments include 2 time points prior to randomization and 2 post randomization and includes collection of urine specimens. The objective of DEPART is to examine associations between urinary biomarkers for emerging contaminants of concern including phthalates, pesticides, and phenols and biomarkers of oxidative stress and inflammation in this population. DEPART also includes metabolomic profiling to investigate potential additional biological mechanisms of toxicity associated with these exposures.
Exposures & analytes
Health outcomes
Demographics
Study analytics
Ranges of measured exposures and phenotypes, and the most prevalent untargeted features in this study.
Exposure ranges
30 analytes| Analyte | Range (log) | Median | n |
|---|---|---|---|
| BP3ng/mL | 23.4 | 281 | |
| BPAng/mL | 1.16 | 281 | |
| BPFng/mL | 0.796 | 281 | |
| BPSng/mL | 0.59 | 281 | |
| BUPBng/mL | 0.047 | 281 | |
| DEPng/mL | 1.465 | 280 | |
| DETPng/mL | 0.153 | 275 | |
| DMPng/mL | 2.45 | 271 | |
| DMTPng/mL | 1.925 | 280 | |
| ETPBng/mL | 0.631 | 281 | |
| MBPng/mL | 16.6 | 281 | |
| MBZPng/mL | 13 | 281 | |
| MCINPng/mL | 2.1 | 281 | |
| MCIOPng/mL | 7.98 | 281 | |
| MCPPng/mL | 2.33 | 281 | |
| MECPPng/mL | 16.9 | 281 | |
| MEHHPng/mL | 11 | 281 | |
| MEHPng/mL | 1.33 | 281 | |
| MEOHPng/mL | 6.98 | 281 | |
| MEPng/mL | 24.3 | 281 | |
| MEPBng/mL | 14.6 | 281 | |
| MIBPng/mL | 14.3 | 281 | |
| NAP1ng/mL | 1.17 | 281 | |
| NAP2ng/mL | 15.5 | 281 | |
| PBAng/mL | 0.244 | 274 | |
| PRPBng/mL | 1.64 | 281 | |
| PYR1ng/mL | 0.073 | 281 | |
| TCCng/mL | 0.032 | 281 | |
| TCPng/mL | 1.12 | 277 | |
| TCSng/mL | 1.82 | 281 |
Phenotype ranges
2 phenotypes| Phenotype | Range | Median | n |
|---|---|---|---|
| adj_eum2endotoxin units per square meter at baseline | 2.2e+3 | 76 | |
| adjugm3PM2.5 concentration in micrograms per meter cubed | 8.824 | 66 |
How exposures relate to phenotypes
Every exposure regressed against every phenotype in this study, with a single study-wide FDR correction across all 60 tests.
phenotype ~ ln(exposure) + sex + ln_creatinine
| Exposure | Phenotype | β | p | FDR q | n |
|---|---|---|---|---|---|
| MCIOP | adj_eum2FDR | +6024.291 | 0.001 | 0.066 | 76 |
| MECPP | adj_eum2FDR | +5799.406 | 0.004 | 0.093 | 76 |
| MEHP | adj_eum2FDR | +7561.565 | 0.005 | 0.093 | 76 |