Environmental Health | |
Construction of environmental risk score beyond standard linear models using machine learning methods: application to metal mixtures, oxidative stress and cardiovascular disease in NHANES | |
Methodology | |
Zhangchen Zhao1  Bhramar Mukherjee2  Sung Kyun Park3  | |
[1] Department of Biostatistics, School of Public Health, University of Michigan, Ann Arbor, MI, USA;Department of Epidemiology, School of Public Health, University of Michigan, 1415 Washington Heights, 48109, Ann Arbor, MI, USA;Department of Biostatistics, School of Public Health, University of Michigan, Ann Arbor, MI, USA;Department of Epidemiology, School of Public Health, University of Michigan, 1415 Washington Heights, 48109, Ann Arbor, MI, USA;Department of Environmental Health Sciences, School of Public Health, University of Michigan, Ann Arbor, MI, USA; | |
关键词: Bayesian additive regression tree (BART); Bayesian kernel machine regression (BKMR); Cardiovascular disease; Elastic-net; Environmental risk score (ERS); Machine learning; Metals; Mixtures; Multipollutants; Super Learner; | |
DOI : 10.1186/s12940-017-0310-9 | |
received in 2017-06-01, accepted in 2017-09-21, 发布年份 2017 | |
来源: Springer | |
【 摘 要 】
BackgroundThere is growing concern of health effects of exposure to pollutant mixtures. We initially proposed an Environmental Risk Score (ERS) as a summary measure to examine the risk of exposure to multi-pollutants in epidemiologic research considering only pollutant main effects. We expand the ERS by consideration of pollutant-pollutant interactions using modern machine learning methods. We illustrate the multi-pollutant approaches to predicting a marker of oxidative stress (gamma-glutamyl transferase (GGT)), a common disease pathway linking environmental exposure and numerous health endpoints.MethodsWe examined 20 metal biomarkers measured in urine or whole blood from 6 cycles of the National Health and Nutrition Examination Survey (NHANES 2003–2004 to 2013–2014, n = 9664). We randomly split the data evenly into training and testing sets and constructed ERS’s of metal mixtures for GGT using adaptive elastic-net with main effects and pairwise interactions (AENET-I), Bayesian additive regression tree (BART), Bayesian kernel machine regression (BKMR), and Super Learner in the training set and evaluated their performances in the testing set. We also evaluated the associations between GGT-ERS and cardiovascular endpoints.ResultsERS based on AENET-I performed better than other approaches in terms of prediction errors in the testing set. Important metals identified in relation to GGT include cadmium (urine), dimethylarsonic acid, monomethylarsonic acid, cobalt, and barium. All ERS’s showed significant associations with systolic and diastolic blood pressure and hypertension. For hypertension, one SD increase in each ERS from AENET-I, BART and SuperLearner were associated with odds ratios of 1.26 (95% CI, 1.15, 1.38), 1.17 (1.09, 1.25), and 1.30 (1.20, 1.40), respectively. ERS’s showed non-significant positive associations with mortality outcomes.ConclusionsERS is a useful tool for characterizing cumulative risk from pollutant mixtures, with accounting for statistical challenges such as high degrees of correlations and pollutant-pollutant interactions. ERS constructed for an intermediate marker like GGT is predictive of related disease endpoints.
【 授权许可】
CC BY
© The Author(s). 2017
【 预 览 】
Files | Size | Format | View |
---|---|---|---|
RO202311102748448ZK.pdf | 1250KB | download | |
12951_2016_246_Article_IEq12.gif | 1KB | Image | download |
Fig. 2 | 523KB | Image | download |
Fig. 4 | 917KB | Image | download |
Fig. 1 | 2578KB | Image | download |
12936_2017_1963_Article_IEq54.gif | 1KB | Image | download |
Fig. 5 | 699KB | Image | download |
Fig. 2 | 1217KB | Image | download |
Fig. 4 | 802KB | Image | download |
Fig. 6 | 2050KB | Image | download |
Fig. 9 | 1857KB | Image | download |
MediaObjects/40798_2023_638_MOESM1_ESM.docx | 53KB | Other | download |
Fig. 5 | 2614KB | Image | download |
Fig. 3 | 198KB | Image | download |
MediaObjects/40249_2023_1144_MOESM1_ESM.docx | 1220KB | Other | download |
Fig. 2 | 3290KB | Image | download |
MediaObjects/12944_2023_1921_MOESM1_ESM.pdf | 34KB | download |
【 图 表 】
Fig. 2
Fig. 3
Fig. 5
Fig. 9
Fig. 6
Fig. 4
Fig. 2
Fig. 5
12936_2017_1963_Article_IEq54.gif
Fig. 1
Fig. 4
Fig. 2
12951_2016_246_Article_IEq12.gif
【 参考文献 】
- [1]
- [2]
- [3]
- [4]
- [5]
- [6]
- [7]
- [8]
- [9]
- [10]
- [11]
- [12]
- [13]
- [14]
- [15]
- [16]
- [17]
- [18]
- [19]
- [20]
- [21]
- [22]
- [23]
- [24]
- [25]
- [26]
- [27]
- [28]
- [29]
- [30]
- [31]
- [32]
- [33]
- [34]
- [35]
- [36]
- [37]
- [38]
- [39]
- [40]
- [41]
- [42]
- [43]
- [44]
- [45]
- [46]
- [47]
- [48]
- [49]
- [50]
- [51]
- [52]
- [53]
- [54]
- [55]
- [56]
- [57]
- [58]
- [59]
- [60]
- [61]
- [62]
- [63]
- [64]
- [65]
- [66]
- [67]
- [68]
- [69]