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1
The findings and conclusions in this presentation are those of the authors and do not necessarily represent the views of the National
Institute for Occupational Safety and Health.
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Can HCP quality be judged by evaluating their component parts?
Can historical data be useful in conducting such evaluations?
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Historic review of 3 plants› 2 automotive plants
› 1 food processor
Covers period from 1970 through 1999
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Historic noise exposure surveys
Historic audiometric test records
Employee work histories
Survey & focus group information on history of hearing conservation programs
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Assigned by Job Title
› Used task-based noise surveys from 1990’s
› Multiple stage extrapolation to earlier jobs and job titles
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Merged historical audiometric testing data with work histories (job titles)
Excellent match for food processor
Poor match for two automotive plants› More than half of all audiometric testing
conducted prior to initial work history
› Possibly due to migration of workers from other plants
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History based on worker focus groups
Four historical HCP components created› % use of hearing protective devices (HPD)
› Audiometric testing frequency (calculated*)
› Frequency & responsiveness of noise monitoring
› Worker education (at shop meetings & testing)
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Leq – cumulative measure of equivalent noise energy› 3 dB increase in TWA doubles exposure
› Does not accommodate uncertainty
› Historical estimates of duration better than intensity
Test alternative measure › Duration of exposure within 5 dB strata
› Weightings determined by the data
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Not addressing “hearing” per se› No need to define a threshold shift› No censorship of data
Use a sensitive yet robust measure› Use most sensitive frequencies› Incorporate bilateral measures› Average across multiple thresholds
Solution › Average at 3, 4 & 6 kHz across both ears
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Reduced data vs. data uncertainty› Do missing work histories = migration
between plants?
› Guessing could introduce large errors – considered too risk
Conclusion: Exclude audiograms with missing work histories
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Used dichotomous variables for all component quality measures› Used “better” vs. “worse” categorization
› Fortunately these varied by time and plant
› Did not necessarily improve over time
› The four components did not necessarily vary together
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Time from Baseline (1st valid) Audiogram
Reasons:› Better captures cumulative exposure
› Less dependent on accuracy of time cut-points for HCP quality measures
› Less dependent on latency of impact
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Variables included:› Intercept + dummy variables for plant
› Baseline (time=0) hearing threshold average
› Age at time of test (time=t)
› Leq + Duration of employment
Results› Duration of employment better predictor of
NIHL
› Majority of noise exposures between 85-95 dB
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Tested stratified model: duration of exposure within 5 dB TWA groups
duration at >=95 dB
duration at <95 dB
Baseline test 1 ….…test 2 …….test 3 ….. test n
Stratified duration for nth audiometric test period for this subject
Only strata significantly different from total exposure duration was for >=95 dB
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Model: duration of exposure by TWA and duration groups (over ‘x’ years in red)
duration at 95+ dB
duration at <95 dB
Baseline test 1 ….…test 2 …….test 3 ….. test n
Two-way stratified duration for nth audiometric test period for this subject
Observed change in the dose-response relationship after 6 years
2020
HCP quality term entered separately for each component
Duration in “Worse” quality HCP (red) does not add to term
Duration in “Better” quality HCP
Baseline test 1 ….…test 2 …….test 3 ….. test n
Duration in “Better” quality HCP for nth audiometric test period for this subject
Interaction terms yielded incoherent results
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Base Model HPD Model Variables Coeff Coeff Intercept -1.89**** -2.18**** Plant X -1.02**** 0.62** Plant Y -0.39* -0.03
Reflecting Individual Characteristics Baseline Threshold -0.03**** -0.03**** Age at Test 0.08**** 0.08****
Reflecting NIHL Duration at <95dB / <=6 (years) 0.60**** 0.77**** Duration at >=95dB / <=6 (years) 0.82**** 1.04****
Duration at <95dB / >6 (years) 0.52**** 0.79**** Duration at >=95dB / >6 (years) 0.44*** 0.69****
Better HPD Use (Years) ----- -0.31****
Coefficients directly reflect average threshold change per variable unit
* p<0.05 **p<0.01 ***p<0.001 ****p<0.0001
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HPD programs effective in reducing NIHL› Reported enforcement of HPD policies
› Did not use information on types of devices No consensus on relative effectiveness of
different devices Dependent on use and acceptance of the
various devices
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Base Model HPD Model Variables Coeff Coeff Intercept -1.89**** -2.18**** Plant X -1.02**** 0.85**** Plant Y -0.39* -0.43*
Reflecting Individual Characteristics Baseline Threshold -0.03**** -0.03**** Age at Test 0.08**** 0.08****
Reflecting NIHL Duration at <95dB / <=6 (years) 0.60**** 0.54**** Duration at >=95dB / <=6 (years) 0.82**** 0.77****
Duration at <95dB / >6 (years) 0.52**** 0.44**** Duration at >=95dB / >6 (years) 0.44*** 0.31*
Better Audiometric Monitoring (Years) ----- 0.13***
Coefficients directly reflect average threshold change per variable unit
* p<0.05 **p<0.01 ***p<0.001 ****p<0.0001
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Apparent reverse association (more testing, more threshold change detected)› Used mean time between tests
Need better descriptors
› Possibly due to artifacts People with poor hearing may resist initial testing Longer term employees & supervisors may resist
testing
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Base Model HPD Model Variables Coeff Coeff Intercept -1.89**** -2.09**** Plant X -1.02**** 0.48* Plant Y -0.39* -0.31
Reflecting Individual Characteristics Baseline Threshold -0.03**** -0.03**** Age at Test 0.08**** 0.08****
Reflecting NIHL Duration at <95dB / <=6 (years) 0.60**** 0.64**** Duration at >=95dB / <=6 (years) 0.82**** 0.83****
Duration at <95dB / >6 (years) 0.52**** 0.53**** Duration at >=95dB / >6 (years) 0.44**** 0.43***
Better Noise Monitoring (Years) ----- -0.13****
Coefficients directly reflect average threshold change per variable unit
* p<0.05 **p<0.01 ***p<0.001 ****p<0.0001
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Apparent effect - BUT› Noise Exposure coefficients basically same
› Larger change in plant coefficient No variation by time within plants Only one plant had a “better program”
› Conclusion: Effect due to confounding
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Base Model HPD Model Variables Coeff Coeff Intercept -1.89**** -1.87**** Plant X -1.02**** -0.99**** Plant Y -0.39* -0.47**
Reflecting Individual Characteristics Baseline Threshold -0.03**** -0.03**** Age at Test 0.08**** 0.08****
Reflecting NIHL Duration at <95dB / <=6 (years) 0.60**** 0.63**** Duration at >=95dB / <=6 (years) 0.82**** 0.84****
Duration at <95dB / >6 (years) 0.52**** 0.54**** Duration at >=95dB / >6 (years) 0.44*** 0.43***
Better Worker Training (Years) ----- -0.04
Coefficients directly reflect average threshold change per variable unit
* p<0.05 **p<0.01 ***p<0.001 ****p<0.0001
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Weak non-significant association› None of the programs were very
satisfactory Sporadic at best “Better” could only be used as a relative
term
› Conclusion: not enough variability
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Were able to obtain interpretable results› Achieved some detail in modeling noise
› Effect of HPD use clearly demonstrated
However, limitations included:› Lack of variation
No quality programs for some components Sometimes no variation in time within plants
› Lack of good measures Need more details in quality and time frame
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Leq may not be suitable for historic studies› Too dependent on accuracy of TWA
Stratified duration shows possibilities› Explained much more NIHL
› Shape of dose response could be explored
› Useful for other time dependent variables E.g. Quality components
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More recent HCPs should have› Better and more detailed records
› More variation with good quality programs
Able to study more components