Project Results for Maternal and Infant Environmental Exposure Project (MIEEP)
Project: Maternal and Infant Environmental Exposure Project (MIEEP)
- Study Group: 92 pregnant women and their infants (65 mother-infant pairs and 27 pregnant women)
- Sample Collection Date: -
Chemical Group: Environmental Phenols
- Measured in: Urine
- Study Group Subset: Pregnant women
Unweighted Results
| Chemical measured | Indicates Exposure to | Adjusted for | Units | Number of people tested | Geometric mean | 95% Confidence Interval | Selected Percentiles | Reporting limit, wet weight | ||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Lower | Upper | 25th | 50th | 75th | 90th | |||||||
| Benzophenone-3 | Benzophenone-3 | NA | μg/L | 89 | 33.0 | 20.5 | 53.2 | 8.41 | 26.6 | 124 | 1320 | 0.50 |
| BPA | Bisphenol A | NA | μg/L | 89 | 1.25 | 0.984 | 1.58 | 0.490 | 1.27 | 3.13 | 4.85 | 0.20 |
| Triclosan | Triclosan | NA | μg/L | 89 | 17.2 | 10.5 | 28.2 | 2.44 | 11.1 | 139 | 445 | 1.0 |
Chemical Group: Metals
- Measured in: Blood
- Study Group Subset: Pregnant women
Unweighted Results
| Chemical measured | Indicates Exposure to | Adjusted for | Units | Number of people tested | Geometric mean | 95% Confidence Interval | Selected Percentiles | Reporting limit, wet weight | ||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Lower | Upper | 25th | 50th | 75th | 90th | |||||||
| Cadmium | Cadmium | NA | μg/L | 77 | 0.22 | 0.19 | 0.24 | 0.16 | 0.22 | 0.31 | 0.38 | 0.14 and 0.15** |
| Lead | Lead | NA | μg/dL | 77 | 0.65 | 0.57 | 0.75 | 0.45 | 0.60 | 0.84 | 1.6 | 0.027 |
| Mercury | Mercury | NA | μg/L | 77 | 0.45 | 0.37 | 0.54 | 0.26 | 0.46 | 0.76 | 1.1 | 0.064 |
Footnotes
- **LOD changed during the time that samples were analyzed for this project.
Chemical Group: Metals
- Measured in: Urine
- Study Group Subset: Pregnant women
Unweighted Results
| Chemical measured | Indicates Exposure to | Adjusted for | Units | Number of people tested | Geometric mean | 95% Confidence Interval | Selected Percentiles | Reporting limit, wet weight | ||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Lower | Upper | 25th | 50th | 75th | 90th | |||||||
| Arsenic | Arsenic | NA | µg/L | 89 | 7.71 | 6.39 | 9.32 | 4.34 | 8.15 | 11.2 | 34.9 | 0.158 |
| Cadmium | Cadmium | Creatinine | μg/g creatinine | 89 | 0.185 | 0.160 | 0.213 | <LOD | 0.178 | 0.257 | 0.364 | 0.105 μg/L |
| Mercury | Mercury | NA | μg/L | 89 | 0.212 | 0.164 | 0.274 | 0.0897 | 0.176 | 0.429 | 0.997 | 0.0522 |
Chemical Group: Organochlorine Pesticides
- Measured in: Serum
- Study Group Subset: Pregnant women
Unweighted Results
| Chemical measured | Indicates Exposure to | Adjusted for | Units | Number of people tested | Geometric mean | 95% Confidence Interval | Selected Percentiles | Reporting limit, wet weight | ||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Lower | Upper | 25th | 50th | 75th | 90th | |||||||
| beta-Hexachlorocyclohexane (beta-HCH) | beta-HCH | Lipids | ng/g lipid | 77 | * | * | * | <LOD | 1.59 | 6.00 | 13.2 | 0.005 ng/mL |
| DDE (para,para) | para,para-DDT and/or para,para-DDE | Lipids | ng/g lipid | 77 | 112 | 85.1 | 149 | 53.0 | 94.0 | 161 | 516 | 0.005 ng/mL |
| DDT (ortho,para) | ortho,para-DDT | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.005 ng/mL |
| DDT (para,para) | para,para-DDT | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | 18.2 | 0.005 ng/mL |
| Hexachlorobenzene (HCB) | HCB | Lipids | ng/g lipid | 77 | 8.26 | 7.58 | 8.99 | 6.50 | 8.43 | 10.1 | 12.5 | 0.034 ng/mL |
| Oxychlordane | Chlordane | Lipids | ng/g lipid | 77 | * | * | * | <LOD | 0.93 | 1.6 | 3.2 | 0.005 ng/mL |
| trans-Nonachlor | Chlordane | Lipids | ng/g lipid | 77 | 1.69 | 1.41 | 2.02 | 1.09 | 1.80 | 2.87 | 4.88 | 0.006 ng/mL |
Footnotes
- *Geometric mean was not calculated because the chemical was found in less than 65% of the study group
Chemical Group: Organophosphate Pesticides
- Measured in: Urine
- Study Group Subset: Pregnant women
Unweighted Results
| Chemical measured | Indicates Exposure to | Adjusted for | Units | Number of people tested | Geometric mean | 95% Confidence Interval | Selected Percentiles | Reporting limit, wet weight | ||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Lower | Upper | 25th | 50th | 75th | 90th | |||||||
| DEDTP | Phorate and others | NA | μg/L | 89 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.10 |
| DEP | Chlorpyrifos, diazinon, and others | NA | μg/L | 89 | 1.41 | 1.10 | 1.80 | <LOD | 1.76 | 3.51 | 6.79 | 0.50 |
| DMDTP | Dimethoate, malathion, methidathion, phosmet, and others | NA | μg/L | 89 | * | * | * | <LOD | <LOD | <LOD | <LOD | 1.0 |
| DMTP | Dimethoate, malathion, methidathion, phosmet, and others | NA | μg/L | 89 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.50 |
| TCPy | Chlorpyrifos | NA | μg/L | 89 | 0.52 | 0.41 | 0.65 | <LOD | 0.53 | 1.2 | 2.2 | 0.20 |
Footnotes
- *Geometric mean was not calculated because the chemical was found in less than 65% of the study group
Chemical Group: Perfluoroalkyl and Polyfluoroalkyl Substances (PFASs)
- Measured in: Serum
- Study Group Subset: Pregnant women
Unweighted Results
| Chemical measured | Indicates Exposure to | Adjusted for | Units | Number of people tested | Geometric mean | 95% Confidence Interval | Selected Percentiles | Reporting limit, wet weight | ||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Lower | Upper | 25th | 50th | 75th | 90th | |||||||
| Et-PFOSA-AcOH | Et-PFOSA-AcOH | NA | ng/mL | 77 | * | * | * | <LOD | 0.012 | 0.021 | 0.026 | 0.011 |
| Me-PFOSA-AcOH | Me-PFOSA-AcOH | NA | ng/mL | 77 | 0.067 | 0.055 | 0.082 | 0.037 | 0.064 | 0.10 | 0.20 | 0.013 |
| PFBS | PFBS | NA | ng/mL | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.022 |
| PFDA | PFDA | NA | ng/mL | 77 | * | * | * | <LOD | <LOD | 0.035 | 0.64 | 0.032 |
| PFDoA | PFDoA | NA | ng/mL | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.036 |
| PFHpA | PFHpA | NA | ng/mL | 77 | * | * | * | <LOD | <LOD | 0.071 | 0.14 | 0.059 |
| PFNA | PFNA | NA | ng/mL | 77 | 0.733 | 0.621 | 0.865 | 0.504 | 0.791 | 1.11 | 1.74 | 0.075 |
| PFOA | PFOA | NA | ng/mL | 77 | * | * | * | <LOD | 0.474 | 0.811 | 1.25 | 0.30 |
| PFOS | PFOS | NA | ng/mL | 77 | 2.55 | 2.20 | 2.95 | 1.78 | 2.43 | 4.11 | 4.90 | 0.083 |
| PFOSA | PFOSA | NA | ng/mL | 77 | 0.019 | 0.016 | 0.022 | 0.012 | 0.017 | 0.026 | 0.049 | 0.01 |
| PFUnDA | PFUnDA | NA | ng/mL | 77 | 0.131 | 0.101 | 0.170 | 0.0730 | 0.165 | 0.261 | 0.474 | 0.01 |
Footnotes
- *Geometric mean was not calculated because the chemical was found in less than 65% of the study group
Chemical Group: Phthalates
- Measured in: Urine
- Study Group Subset: Pregnant women
Unweighted Results
| Chemical measured | Indicates Exposure to | Adjusted for | Units | Number of people tested | Geometric mean | 95% Confidence Interval | Selected Percentiles | Reporting limit, wet weight | ||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Lower | Upper | 25th | 50th | 75th | 90th | |||||||
| MBzP | Benzylbutyl phthalate (BzBP) | NA | μg/L | 89 | 7.73 | 5.84 | 10.2 | 2.72 | 6.54 | 18.4 | 53.4 | 0.25 |
| MCHP | Dicyclohexyl phthalate (DCHP) | NA | μg/L | 89 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.50 |
| MCPP | Di-n-octyl phthalate (DnOP) | NA | μg/L | 89 | 0.87 | 0.72 | 1.05 | 0.48 | 0.75 | 1.2 | 2.8 | 0.125 |
| MECPP | Di-2-ethylhexyl phthalate (DEHP) | NA | μg/L | 89 | 17.1 | 13.5 | 21.7 | 8.09 | 14.6 | 29.4 | 68.8 | 0.50 |
| MEP | Diethyl phthalate (DEP) | NA | μg/L | 89 | 95.5 | 69.3 | 132 | 34.7 | 103 | 254 | 679 | 8.0 |
| MnBP | Dibutyl phthalate (DBP), Benzylbutyl phthalate (BzBP) | NA | μg/L | 89 | 16.3 | 13.0 | 20.5 | 6.59 | 16.2 | 34.2 | 60.8 | 2.0 |
Footnotes
- *Geometric mean was not calculated because the chemical was found in less than 65% of the study group
Chemical Group: Polybrominated Diphenyl Ethers (PBDEs)
- Measured in: Serum
- Study Group Subset: Pregnant women
Unweighted Results
| Chemical measured | Indicates Exposure to | Adjusted for | Units | Number of people tested | Geometric mean | 95% Confidence Interval | Selected Percentiles | Reporting limit, wet weight | ||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Lower | Upper | 25th | 50th | 75th | 90th | |||||||
| BDE 017 | BDE 17 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.005 ng/mL |
| BDE 028 | BDE 28 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | 0.75 | 1.6 | 0.005 ng/mL |
| BDE 047 | BDE 47 | Lipids | ng/g lipid | 77 | 9.56 | 7.54 | 12.1 | 4.67 | 8.34 | 16.0 | 33.0 | 0.023 ng/mL |
| BDE 066 | BDE 66 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.005 ng/mL |
| BDE 085 | BDE 85 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.005 ng/mL |
| BDE 099 | BDE 99 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | 2.74 | 5.02 | 9.92 | 0.019 ng/mL |
| BDE 100 | BDE 100 | Lipids | ng/g lipid | 77 | 2.17 | 1.70 | 2.77 | 0.960 | 1.96 | 3.95 | 8.11 | 0.005 ng/mL |
| BDE 153 | BDE 153 | Lipids | ng/g lipid | 77 | 2.64 | 2.01 | 3.47 | 0.980 | 1.94 | 7.66 | 14.9 | 0.005 ng/mL |
| BDE 154 | BDE 154 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.007 ng/mL |
| BDE 183 | BDE 183 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.007 ng/mL |
| BDE 196 | BDE 196 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.007 ng/mL |
| BDE 197 | BDE 197 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | 0.93 | 1.5 | 0.007 ng/mL |
| BDE 201 | BDE 201 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.007 ng/mL |
| BDE 202 | BDE 202 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.007 ng/mL |
| BDE 203 | BDE 203 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.007 ng/mL |
| BDE 206 | BDE 206 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.009 ng/mL |
| BDE 207 | BDE 207 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | 2.07 | 0.009 ng/mL |
| BDE 208 | BDE 208 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.009 ng/mL |
| BDE 209 | BDE 209 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | 5.41 | 9.31 | 13.5 | 0.045 ng/mL |
Footnotes
- *Geometric mean was not calculated because the chemical was found in less than 65% of the study group
Chemical Group: Polychlorinated Biphenyls (PCBs)
- Measured in: Serum
- Study Group Subset: Pregnant women
Unweighted Results
| Chemical measured | Indicates Exposure to | Adjusted for | Units | Number of people tested | Geometric mean | 95% Confidence Interval | Selected Percentiles | Reporting limit, wet weight | ||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Lower | Upper | 25th | 50th | 75th | 90th | |||||||
| PCB 066 | PCB 66 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.009 ng/mL |
| PCB 074 | PCB 74 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | 1.1 | 0.008 ng/mL |
| PCB 099 | PCB 99 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | 2.23 | 0.014 ng/mL |
| PCB 101 | PCB 101 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | 2.63 | 0.016 ng/mL |
| PCB 105 | PCB 105 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.010 ng/mL |
| PCB 118 | PCB 118 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | 2.02 | 2.97 | 0.014 ng/mL |
| PCB 138 | PCB 138 | Lipids | ng/g lipid | 77 | 1.94 | 1.69 | 2.22 | 1.29 | 1.90 | 2.63 | 4.15 | 0.006 ng/mL |
| PCB 153 | PCB 153 | Lipids | ng/g lipid | 77 | 2.98 | 2.57 | 3.46 | 1.95 | 3.02 | 4.29 | 6.59 | 0.011 ng/mL |
| PCB 156 | PCB 156 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | 0.89 | 0.005 ng/mL |
| PCB 170 | PCB 170 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | 0.65 | 0.92 | 1.7 | 0.005 ng/mL |
| PCB 180 | PCB 180 | Lipids | ng/g lipid | 77 | 1.97 | 1.67 | 2.31 | 1.27 | 1.79 | 2.90 | 4.91 | 0.007 ng/mL |
| PCB 183 | PCB 183 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | <LOD | 0.012 ng/mL |
| PCB 187 | PCB 187 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | 1.2 | 1.7 | 0.009 ng/mL |
| PCB 194 | PCB 194 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | <LOD | 1.0 | 0.007 ng/mL |
| PCB 203 | PCB 203 | Lipids | ng/g lipid | 77 | * | * | * | <LOD | <LOD | 0.88 | 1.4 | 0.007 ng/mL |
Footnotes
- *Geometric mean was not calculated because the chemical was found in less than 65% of the study group
Chemical Group: Polycyclic Aromatic Hydrocarbons (PAHs)
- Measured in: Urine
- Study Group Subset: Pregnant women
Unweighted Results
| Chemical measured | Indicates Exposure to | Adjusted for | Units | Number of people tested | Geometric mean | 95% Confidence Interval | Selected Percentiles | Reporting limit, wet weight | ||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Lower | Upper | 25th | 50th | 75th | 90th | |||||||
| 1-NAP | Naphthalene | NA | ng/L | 88 | 1020 | 800 | 1300 | 465 | 858 | 1940 | 4060 | 25.0 |
| 1-PHEN | Phenanthrene | NA | ng/L | 88 | 193 | 161 | 232 | 107 | 198 | 323 | 588 | 10.0 |
| 1-PYR | Pyrene | NA | ng/L | 88 | 186 | 153 | 227 | 88.2 | 211 | 334 | 598 | 20.0 |
| 2-FLUO | Fluorene | NA | ng/L | 88 | 192 | 157 | 235 | 96.0 | 188 | 311 | 529 | 20.0 |
| 2-NAP | Naphthalene | NA | ng/L | 88 | 6490 | 5140 | 8190 | 2780 | 6780 | 14000 | 23700 | 20.0 |
| 2-PHEN | Phenanthrene | NA | ng/L | 88 | 99.4 | 85.9 | 115 | 60.6 | 94.4 | 159 | 235 | 10.0 |
| 3-FLUO | Fluorene | NA | ng/L | 88 | 54.8 | 43.7 | 68.8 | 23.5 | 45.8 | 106 | 212 | 20.0 |
| 3-PHEN | Phenanthrene | NA | ng/L | 88 | 69.4 | 57.3 | 84.0 | 34.1 | 70.2 | 109 | 190 | 10.0 |
| 9-FLUO | Fluorene | NA | ng/L | 88 | 535 | 440 | 651 | 272 | 536 | 814 | 1370 | 37.0 |
Chemical Group: Pyrethroid Pesticides
- Measured in: Urine
- Study Group Subset: Pregnant women
Unweighted Results
| Chemical measured | Indicates Exposure to | Adjusted for | Units | Number of people tested | Geometric mean | 95% Confidence Interval | Selected Percentiles | Reporting limit, wet weight | ||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Lower | Upper | 25th | 50th | 75th | 90th | |||||||
| 3-Phenoxybenzoic acid (3-PBA) | Cyhalothrin, cypermethrin, deltamethrin, fenpropathrin, permethrin, and/or tralomethrin | NA | μg/L | 89 | * | * | * | <LOD | <LOD | 0.46 | 2.6 | 0.40 |
Footnotes
- *Geometric mean was not calculated because the chemical was found in less than 65% of the study group