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. 2020 May 31;11:100590. doi: 10.1016/j.ssmph.2020.100590

Table 3.

Effects of the Automobile NOx Law on fetal and infant health outcomes.


(Air Quality Bureau of the Environment Agency and Automobile NOx Law Research Group, 19941) FDR
(2) LBWR
(3) IMR
(4) NMR
[36.79] [6.40] [4.46] [2.45]
Regulation 2.593 −0.088 −0.017 −0.003
(2.799) (0.315) (0.916) (0.685)
I (Year = 1991) −1.179 0.168 −0.246 −0.310
(1.497) (0.171) (0.524) (0.361)
I(Year = 1993) −1.655 0.624*** −0.255 −0.249
(1.521) (0.191) (0.538) (0.382)
I(Year = 2000) −4.397** 2.290*** −1.055** −0.360
(2.029) (0.227) (0.450) (0.386)
Regulation×I(Year = 1991) −1.501 0.202 −0.026 −0.078
(1.570) (0.183) (0.545) (0.377)
Regulation×I(Year = 1993) −4.218** 0.105 0.188 0.019
(1.637) (0.201) (0.567) (0.401)
Regulation×I(Year = 2000) −7.094*** 0.060 0.115 −0.397
(2.130) (0.238) (0.502) (0.404)
Control variables Yes Yes Yes Yes
City-county FE Yes Yes Yes Yes
Observations 1559 1559 1559 1559
Municipalities 390 390 390 390
Adj. R-squared 0.5595 0.5759 0.0276 0.0392

Notes: FDR, LBWR, IMR, and NMR represent the fetal death rate, low-birth weight rate, infant mortality rate, and neonatal mortality rate, respectively. The regression shown in Column (1) is weighted by the number of births, whereas the regressions shown in Columns (2)–(4) are weighted by the number of live births. The mean values of the outcome variables in regulated areas in the pre-intervention period are reported in brackets. The control variables include the coverage of hospitals and proportion of households receiving welfare benefits. ***, **, and * represent statistical significance at the 1%, 5%, and 10% levels, respectively. Standard errors clustered at the municipal level are in parentheses.