Table 2.
Subgroups | No. of studies | Heterogeneity test | Summary OR (95 % CI) | Hypothesis test | I2 (%) | Egger’s test | |||
---|---|---|---|---|---|---|---|---|---|
Q | P | Z | P | t | P | ||||
Exposure during the entire pregnancy | 13 | 80.51 | <0.001 | 1.13* (1.03–1.24) | 2.59 | 0.010 | 91.4 | 2.20 | 0.051 |
Specific trimester | |||||||||
First trimester exposure | 10 | 89.14 | <0.001 | 1.08 (0.92–1.26) | 0.96 | 0.334 | 91.3 | 0.68 | 0.517 |
Second trimester exposure | 5 | 138.69 | <0.001 | 1.09 (0.82–1.44) | 0.60 | 0.548 | 98.7 | 0.311 | 0.776 |
Third trimester exposure | 9 | 44.83 | <0.001 | 1.08** (0.99–1.17) | 1.70 | 0.089 | 92.1 | 1.58 | 0.157 |
First month of gestation | 3 | 22.03 | <0.001 | 1.10 (0.92–1.30) | 1.03 | 0.301 | 91.0 | 0.58 | 0.666 |
Within one month before birth | 6 | 51.49 | <0.001 | 1.01 (0.86–1.19) | 0.09 | 0.926 | 96.8 | 0.03 | 0.980 |
Exposure assessment methoda | |||||||||
Individual exposure | 3 | 4.94 | 0.085 | 1.11 (0.89–1.37) | 0.93 | 0.352 | 61.3 | 1.74 | 0.332 |
Semi-individual exposure | 9 | 55.86 | <0.001 | 1.14 (0.97–1.35) | 1.56 | 0.119 | 93.0 | 0.35 | 0.737 |
Regional level | 4 | 46.19 | <0.001 | 1.07 (0.94–1.23) | 1.00 | 0.319 | 93.8 | 0.11 | 0.921 |
Study designa | |||||||||
Retrospective studies | 9 | 70.98 | <0.001 | 1.10* (1.01–1.21) | 2.12 | 0.034 | 93.3 | 2.31 | 0.055 |
Prospective studies | 4 | 4.64 | 0.201 | 1.42* (1.08–1.85) | 2.52 | 0.012 | 39.5 | 0.10 | 0.927 |
Study settinga | |||||||||
USA | 8 | 50.49 | <0.001 | 1.16* (1.05–1.29) | 2.73 | 0.006 | 90.6 | 1.80 | 0.121 |
Others | 5 | 7.90 | 0.095 | 0.98 (0.95–1.01) | 1.11 | 0.268 | 0.1 | 1.62 | 0.205 |
a: All of these subgroup analyses were conducted for the studies that assessed the association between PM2.5 exposure during the entire pregnancy and preterm birth. All of these estimates were ORs for each 10 μg/m3 increment of PM2.5 exposure during the entire pregnancy
*: p < 0.05
**: 0.05 < p < 0.10