Guski |
62 |
The evidence of exposure–response relations between noise levels and % HA is moderate (aircraft, railway) or low (road traffic, wind turbines). The evidence of correlations between noise levels and annoyance raw scores is high (aircraft, railway) or moderate (road traffic, wind turbines) |
A.8 |
Hays |
narrative |
oil and gas activities produce noise at levels that may increase the risk of adverse health outcomes, including annoyance, sleep disturbance, and cardiovascular diseases |
I.5 |
Hume |
narrative |
annoyance is the mediating factor between noise exposure and cardiovascular diseases with annoyance has associations with a number of cofactors such as noise sensitivity, negative affectivity and mental health |
I.6 |
Lercher |
narrative |
important modifiers may partly be responsible for the large variations found in the noise health effects (socio-demographic factors, length of exposure, bedroom.) |
I.6 |
Schmidt |
36 |
a dose–response relationship between wind turbine noise linked to noise annoyance, sleep disturbance and possibly even psychological distress is present in the literature |
A.6 |