| Literature DB >> 29319010 |
Wenjia Wei1, Stefanie Heinze2, Doris G Gerstner1, Sandra M Walser1, Dorothee Twardella3, Christina Reiter1, Veronika Weilnhammer1, Carmelo Perez-Alvarez4, Thomas Steffens4, Caroline E W Herr5.
Abstract
BACKGROUND: Studies investigating leisure noise effect on extended high frequency hearing are insufficient and they have inconsistent results. The aim of this study was to investigate if extended high-frequency hearing threshold shift is related to audiometric notch, and if total leisure noise exposure is associated with extended high-frequency hearing threshold shift.Entities:
Mesh:
Year: 2017 PMID: 29319010 PMCID: PMC5771058 DOI: 10.4103/nah.NAH_28_17
Source DB: PubMed Journal: Noise Health ISSN: 1463-1741 Impact factor: 0.867
Distribution of sociodemographic variables and noise exposure in 278 participants
| Variables | Categories |
|
|---|---|---|
| Age (years) in O III | 18 or 19 | 3 (1.1) |
| 20 | 115 (41.4) | |
| 21 | 122 (43.9) | |
| 22 or 23 | 38 (13.7) | |
| Sex | Male | 130 (46.8) |
| Female | 148 (53.2) | |
| School years at baseline | 12 | 184 (66.2) |
| 10–11 | 52 (18.7) | |
| 9 | 42 (15.1) | |
| Firecracker exposure in O III | Yes | 174 (62.6) |
| No | 104 (37.4) | |
| Total leisure noise exposure in O IIIa (dB(A)) | <80 | 25 (9.0) |
| ≥80 to <85 | 49 (17.6) | |
| ≥85 to <90 | 109 (39.2) | |
| ≥90 | 95 (34.2) |
O III: the 2nd follow-up of Ohrkan study. aThe mean equivalent A-weighted continuous sound pressure level is extrapolated to a 40-h working week (L Aeq,40h).
Description of hearing threshold level (dB) at each extended high frequency and bivariate logistic regression for the association of hearing threshold shift and audiometric notcha
| Frequency (kHz) | Right ear | Left ear | Hearing threshold shiftb
| Odds ratio (95% CI) | ||||
|---|---|---|---|---|---|---|---|---|
|
|
| |||||||
| Mean ± SD | Min | Max | Mean ± SD | Min | Max | |||
| 9 | 7.03 ± 6.80 | 0 | 40 | 7.82 ± 8.15 | 0 | 45 | 40 (14.39) | 2.33 (0.59–9.19) |
| 10c | 5.31 ± 7.21 | −5 | 55 | 6.44 ± 8.12 | −5 | 45 | 31 (11.15) | 5.08 (1.40–18.48) |
| 11.2c | 5.41 ± 6.79 | 0 | 45 | 6.85 ± 8.18 | −5 | 55 | 31 (11.15) | 7.72 (2.2–27.07) |
| 12.5 | 4.64 ± 7.02 | 0 | 50 | 5.43 ± 8.22 | 0 | 55 | 30 (10.79) | 8.07 (2.30–28.33) |
| 14 | 6.58 ± 9.04 | 0 | 40 | 6.04 ± 9.55 | 0 | 55 | 50 (17.99) | 4.11 (1.20–14.06) |
| 16 | 7.52 ± 10.58 | 0 | 50 | 8.35 ± 11.14 | 0 | 50 | 72 (25.90) | 1.67 (0.48–5.89) |
Identified by Niskar criteria: threshold values at 0.5 and 1 kHz were <15 dB hearing level (better), and the maximum (poorer) threshold value at 3, 4, or 6 kHz was at least 15 dB higher (poorer) than the highest (poorest) threshold value for 0.5 and 1 kHz, and the threshold value at 8 kHz was at least 10 dB lower (better) than the maximum (poorest) threshold value for 3, 4, or 6 kHz. bParticipants with hearing threshold level >15 dB in at least one ear in each frequency. cThe difference of hearing threshold level between right and left ear is significant.
Figure 1Mean hearing threshold level (dB) at extended high frequencies in left ear by sex
Figure 2Mean hearing threshold level (dB) at extended high frequencies in right ear by sex
Odds ratios (95% CI) in logistic regression for the association of total leisure noise exposure and hearing threshold shift at extended high frequencies
| Frequency (kHz) | Total leisure noise (dB(A)) |
| Bivariate modela | Multivariate model 1b | Multivariate model 2c |
|---|---|---|---|---|---|
| 9 | <85 | 74 (26.6) | 1.00 | 1.00 | 1.00 |
| 85 to <90 | 109 (39.2) | 0.71 (0.30–1.70) | 0.68 (0.28–1.65) | 0.71 (0.29–1.73) | |
| ≥90 | 95 (34.2) | 1.25 (0.55–2.86) | 1.20 (0.52–2.77) | 1.26 (0.54–2.93) | |
| 10 | <85 | 74 (26.6) | 1.00 | 1.00 | 1.00 |
| 85 to <90 | 109 (39.2) | 0.81 (0.32–2.07) | 0.82 (0.32–2.13) | 0.90 (0.34–2.36) | |
| ≥90 | 95 (34.2) | 0.95 (0.37–2.42) | 0.93 (0.36–2.40) | 1.02 (0.39–2.67) | |
| 11.2 | <85 | 74 (26.6) | 1.00 | 1.00 | 1.00 |
| 85 to <90 | 109 (39.2) | 0.73 (0.28–1.89) | 0.78 (0.30–2.07) | 0.82 (0.31–2.19) | |
| ≥90 | 95 (34.2) | 1.04 (0.42–2.63) | 1.07 (0.42–2.72) | 1.12 (0.44–2.89) | |
| 12.5 | <85 | 74 (26.6) | 1.00 | 1.00 | 1.00 |
| 85 to <90 | 109 (39.2) | 0.93 (0.35–2.43) | 0.95 (0.36–2.53) | 0.98 (0.37–2.64) | |
| ≥90 | 95 (34.2) | 1.08 (0.41–2.84) | 1.09 (0.41–2.90) | 1.13 (0.42–3.03) | |
| 14 | <85 | 74 (26.6) | 1.00 | 1.00 | 1.00 |
| 85 to <90 | 109 (39.2) | 0.72 (0.34–1.52) | 0.70 (0.33–1.50) | 0.74 (0.34–1.59) | |
| ≥90 | 95 (34.2) | 0.73 (0.34–1.59) | 0.71 (0.33–1.55) | 0.75 (0.34–1.65) | |
| 16 | <85 | 74 (26.6) | 1.00 | 1.00 | 1.00 |
| 85 to <90 | 109 (39.2) | 0.93 (0.48–1.82) | 0.95 (0.48–1.87) | 1.00 (0.50–1.98) | |
| ≥90 | 95 (34.2) | 0.91 (0.46–1.82) | 0.91 (0.45–1.82) | 0.96 (0.48–1.95) |
No covariate in bivariate model, only total leisure noise exposure. bAdjusted for sex and school type. cAdjusted for sex, school type and firecracker exposure.