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

Table A23.

Summary of findings table for the association between rail traffic noise exposure and the prevalence of ischaemic heart disease.

Question Does Exposure to Rail Traffic Noise Increase the Risk of IHD
People Adult population (men and women)
Setting Residential setting: people living several cities in Europe
Outcome The prevalence of IHD
Summary of findings RR per 10 dB increase in road traffic noise level (LDEN) 1.18 (95% CI: 0.82–1.68) per 10 dB
Number of participants (# studies) 13,241 (4)
Number of cases 283
Rating Adjustment to rating
Quality assessment Starting rating 4 cross-sectional studies 2 (low) #
Factors decreasing confidence Risk of bias Serious a Downgrading
Inconsistency Serious b Downgrading
Indirectness None c No downgrading
Imprecision Minor d No downgrading
Publication bias NA e No downgrading
Factors increasing confidence Strength of association Large, but non-significant f No upgrading
Exposure-response gradient Evidence of a non-significant exposure-response gradient f No upgrading
Possible confounding No conclusions can be drawn g No upgrading
Overall judgement of quality of evidence 0 (very low)

# Since only cross-sectional studies were available, we started with a grading of “low” (2); a Response rates were in two of the four studies below 60%. In all studies, IHD was ascertained by means of a questionnaire only; b Results across studies differed in the magnitude and direction of effect estimates (see Figure 5.7 of the complete review). This was confirmed by the results of the heterogeneity analyses, indicating “moderate” heterogeneity (I2residual = 57.4%); c The studies assessed population, exposure and outcome of interest; d We considered the results to be less precise: the 95% CI contained values > 1.25; however, we considered the sample size to be sufficiently large; e Due to the low number of available effect estimates, it was not possible to test for publication bias or small study bias; f Most studies found that the risk of IHD increased when rail traffic noise level increased (RR per 10 dB > 1). There was evidence of a non-significant exposure-response gradient: After aggregating the results of the evaluated studies, we found a non-significant effect size of 1.18 per 10 dB. The noise range of the studies under evaluation was 30–80 dB. This means that if rail traffic noise level increases from 30 to 80 dB, the RR = 2.29; g We were not able to draw any conclusions whether possible residual confounders or biases would reduce our effect estimate.