TY - JOUR
T1 - A cross-validation based approach for estimating specific gravity in elementary-school aged children using a nonlinear model
AU - Busgang, Stefanie A.
AU - Andra, Syam S.
AU - Curtin, Paul
AU - Colicino, Elena
AU - Mazzella, Matthew J.
AU - Bixby, Moira
AU - Sanders, Alison P.
AU - Meeker, John D.
AU - Hauptman, Marissa
AU - Yelamanchili, Shirisha
AU - Phipatanakul, Wanda
AU - Gennings, Chris
N1 - Funding Information:
We would like to thank the Centers for Disease Control and Prevention (CDC) for conducting NHANES, as well as the participants of the 2015–2016 NHANES cycle for making this research possible. We would like to thank the participants of the School Inner-City Asthma Intervention Study. Finally, we would like to express gratitude to the National Institute of Environmental Health Sciences (NIEHS) for providing support for HHEAR. This work was supported in part by funding from NIH/NIEHS: U2CES026561, U2CES026553, U2CES026555, R00ES027508, R01AI073964, R01AI073964-02S1, K24AI106822, K23ES031663, U01AI110397, and P30ES000002. Dr. Hauptman was also supported by the American Academy of Pediatrics (AAP) and funded in part by cooperative agreement award with the Centers for Disease Control and Prevention/Agency for Toxic Substances and Disease Registry (CDC/ATSDR) FAIN:NU61TS000296. The U.S. Environmental Protection Agency (U.S.EPA) supports the Pediatric Environmental Health Specialty Units (PEHSUs) by providing partial funding to the ATSDR under Inter-Agency Agreement DW-75-95877701. The findings and conclusions presented have not been formally disseminated by CDC/ATSDR or EPA and should not be construed to represent any agency determination or policy. Use of trade names that may be mentioned is for identification only and does not imply endorsement by the CDC/ATSDR or EPA.
Funding Information:
We would like to thank the Centers for Disease Control and Prevention (CDC) for conducting NHANES, as well as the participants of the 2015–2016 NHANES cycle for making this research possible. We would like to thank the participants of the School Inner-City Asthma Intervention Study. Finally, we would like to express gratitude to the National Institute of Environmental Health Sciences (NIEHS) for providing support for HHEAR. This work was supported in part by funding from NIH / NIEHS : U2CES026561 , U2CES026553 , U2CES026555 , R00ES027508 , R01AI073964 , R01AI073964-02S1 , K24AI106822 , K23ES031663 , U01AI110397 , and P30ES000002 . Dr. Hauptman was also supported by the American Academy of Pediatrics (AAP) and funded in part by cooperative agreement award with the Centers for Disease Control and Prevention / Agency for Toxic Substances and Disease Registry ( CDC/ATSDR ) FAIN:NU61TS000296 . The U.S. Environmental Protection Agency (U.S.EPA) supports the Pediatric Environmental Health Specialty Units (PEHSUs) by providing partial funding to the ATSDR under Inter-Agency Agreement DW-75-95877701 . The findings and conclusions presented have not been formally disseminated by CDC/ATSDR or EPA and should not be construed to represent any agency determination or policy. Use of trade names that may be mentioned is for identification only and does not imply endorsement by the CDC/ATSDR or EPA.
Publisher Copyright:
© 2022
PY - 2023/1/15
Y1 - 2023/1/15
N2 - Environmental research often relies on urinary biomarkers which require dilution correction to accurately measure exposures. Specific gravity (SG) and creatinine (UCr) are commonly measured urinary dilution factors. Epidemiologic studies may assess only one of these measures, making it difficult to pool studies that may otherwise be able to be combined. Participants from the National Health and Nutrition Examination Survey 2007–2008 cycle were used to perform k-fold validation of a nonlinear model estimating SG from UCr. The final estimated model was applied to participants from the School Inner-City Asthma Intervention Study, who submitted urinary samples to the Children's Health Exposure Analysis Resource. Model performance was evaluated using calibration metrics to determine how closely the average estimated SG was to the measured SG. Additional models, with interaction terms for age, sex, body mass index, race/ethnicity, relative time of day when sample was collected, log transformed 4-(Methylnitrosamino)-1-(3-pyridyl)-1-butanol (NNAL), and asthma status were estimated and assessed for improvement. The association between monobenzyl phthalate (MBZP) and asthma symptom days, controlling for measured UCr, measured SG, and each estimated SG were compared to assess validity of the estimated SG. The model estimating SG from UCr alone, resulted in a beta estimate of 1.10 (95% CI: 1.01, 1.19), indicating agreement between model-predicted SG and measured SG. Inclusion of age and sex in the model improved estimation (β = 1.06, 95% CI: 0.98, 1.15). The full model accounting for all interaction terms with UCr resulted in the best agreement (β = 1.01, 95% CI: 0.93,1.09). Associations between MBZP and asthma symptoms days, controlling for each estimated SG, were within the range of effect estimates when controlling for measured SG and measured UCr (Rate ratios = 1.28–1.34). Our nonlinear modeling provides opportunities to estimate SG in studies that measure UCr or vice versa, enabling data pooling despite differences in urine dilution factors.
AB - Environmental research often relies on urinary biomarkers which require dilution correction to accurately measure exposures. Specific gravity (SG) and creatinine (UCr) are commonly measured urinary dilution factors. Epidemiologic studies may assess only one of these measures, making it difficult to pool studies that may otherwise be able to be combined. Participants from the National Health and Nutrition Examination Survey 2007–2008 cycle were used to perform k-fold validation of a nonlinear model estimating SG from UCr. The final estimated model was applied to participants from the School Inner-City Asthma Intervention Study, who submitted urinary samples to the Children's Health Exposure Analysis Resource. Model performance was evaluated using calibration metrics to determine how closely the average estimated SG was to the measured SG. Additional models, with interaction terms for age, sex, body mass index, race/ethnicity, relative time of day when sample was collected, log transformed 4-(Methylnitrosamino)-1-(3-pyridyl)-1-butanol (NNAL), and asthma status were estimated and assessed for improvement. The association between monobenzyl phthalate (MBZP) and asthma symptom days, controlling for measured UCr, measured SG, and each estimated SG were compared to assess validity of the estimated SG. The model estimating SG from UCr alone, resulted in a beta estimate of 1.10 (95% CI: 1.01, 1.19), indicating agreement between model-predicted SG and measured SG. Inclusion of age and sex in the model improved estimation (β = 1.06, 95% CI: 0.98, 1.15). The full model accounting for all interaction terms with UCr resulted in the best agreement (β = 1.01, 95% CI: 0.93,1.09). Associations between MBZP and asthma symptoms days, controlling for each estimated SG, were within the range of effect estimates when controlling for measured SG and measured UCr (Rate ratios = 1.28–1.34). Our nonlinear modeling provides opportunities to estimate SG in studies that measure UCr or vice versa, enabling data pooling despite differences in urine dilution factors.
KW - Calibration metrics
KW - Data pooling
KW - Dilution factors
UR - http://www.scopus.com/inward/record.url?scp=85142749076&partnerID=8YFLogxK
U2 - 10.1016/j.envres.2022.114793
DO - 10.1016/j.envres.2022.114793
M3 - Article
C2 - 36414110
AN - SCOPUS:85142749076
SN - 0013-9351
VL - 217
JO - Environmental Research
JF - Environmental Research
M1 - 114793
ER -