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. 2018 Feb 22;15(2):379. doi: 10.3390/ijerph15020379

Table 3.

Noise exposure and the risk of IHD: summary of findings.

Noise Source Outcome $ Number of Study Design (s) * RR per 10 dB (95% CI) Participants (Cases) Quality of Evidence
Air traffic Prev 2 CS 1.07 (0.94–1.23) 14,098 (340)
Inc 2 ECO 1.09 (1.04–1.15) 9,619,082 (158,977)
Mort 2 ECO 1.04 (0.97–1.12) 3,897,645 (26,066)
1 CO 1.04 (0.98–1.11) 4,580,311(15,532)
Road traffic Prev 8 CS 1.24 (1.08–1.42) 25,682 (1614)
Inc 1 ECO 1.12 (0.85–1.48) 262,830 (418)
3 CO, 4CC 1.08 (1.01–1.15) 67,224 (7033)
Mort 1 CC, 2 CO 1.05 (0.97–1.13) 532,268 (6884)
Rail traffic Prev 4 CS 1.18 (0.82–1.68) 13,241 (283)

$ Outcome: Prev = prevalence of IHD, Inc = incidence of IHD, Mort = mortality due to IHD; * ECO = ecological study, CS = cross-sectional study, CC = case-control study, CO = cohort study; : RR = Relative Risk per 10 decibel (dB change in noise level, 95% CI = 95% Confidence Interval. For air, road –and, rail traffic, noise levels are expressed in LDEN.; GRADE Working Group Grades of Evidence: High quality (⊕⊕⊕⊕): Further research is very unlikely to change our confidence in the estimate of effect, Moderate Quality (⊕⊕⊕): Further research is likely to have an important impact on our confidence in the estimate of effect and may change the estimate, Low Quality (⊕⊕): Further research is very likely to have an important impact on our confidence in the estimate of effect and is likely to change the estimate, Very low quality (⊕): We are very uncertain about the estimate.