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  • 标题:Noise-induced hearing loss in construction workers being assessed for Hand-arm Vibration Syndrome.
  • 作者:House, Ronald A. ; Sauve, John T. ; Jiang, Depeng
  • 期刊名称:Canadian Journal of Public Health
  • 印刷版ISSN:0008-4263
  • 出版年度:2010
  • 期号:May
  • 语种:English
  • 出版社:Canadian Public Health Association
  • 摘要:Many workers are exposed to high noise levels and may develop noise-induced hearing loss (NIHL). (1,2) Tak et al. (3) estimated that, after the manufacturing sector, the construction sector had the greatest number of workers occupationally exposed to noise in the US. Construction workers in Canada are similarly exposed to high noise levels (4) and at risk of NIHL. (5,6) In construction work, the use of hand-held vibrating tools is an important source of noise exposure. (4)
  • 关键词:Ambulatory care facilities;Clinics;Construction workers;Employers;Environmental health;Hand;Hand injuries;Health facilities construction;Hearing loss;Medical research;Medicine, Experimental;Noise control;Occupational health services;Public health;Safety regulations;Vibration;Vibration (Physics);Vibration syndrome

Noise-induced hearing loss in construction workers being assessed for Hand-arm Vibration Syndrome.


House, Ronald A. ; Sauve, John T. ; Jiang, Depeng 等


Many workers are exposed to high noise levels and may develop noise-induced hearing loss (NIHL). (1,2) Tak et al. (3) estimated that, after the manufacturing sector, the construction sector had the greatest number of workers occupationally exposed to noise in the US. Construction workers in Canada are similarly exposed to high noise levels (4) and at risk of NIHL. (5,6) In construction work, the use of hand-held vibrating tools is an important source of noise exposure. (4)

Exposure to hand-arm vibration may result in Hand-Arm Vibration Syndrome (HAVS) which is comprised of vascular, neurological and musculoskeletal components. (7,8) The main vascular component consists of cold-induced blanching of the fingers, a form of secondary Raynaud's phenomenon which is often referred to as Vibration White Finger (VWF). (9) Several studies have found that in workers exposed to both noise and hand-arm vibration, those workers with VWF have greater hearing loss than workers without VWF, after controlling for noise exposure. (10-15) However a well-designed study by Pyykko et al. (16 found that the permanent hearing loss in workers exposed to noise and vibration did not exceed the permanent hearing loss from exposure to noise only. Therefore it appears that VWF might be a marker for increased individual susceptibility to noise-induced hearing loss without the vibration conferring increased risk of hearing loss from noise exposure. (17,18)

The Occupational Health Clinic at St. Michael's Hospital in Toronto, Ontario has a comprehensive program to assess workers for HAVS. Most of the construction workers assessed for HAVS have not had audiometry at work and therefore the clinic offers audiometry to these workers as a means of case finding for NIHL. This study was carried out to assess the extent of NIHL in these construction workers and to examine possible predictors, in particular the duration of work in construction and the severity of VWF.

METHODS

A total of 191 construction workers were assessed for HAVS between January 1, 2006 and December 31, 2007. All had been exposed to noise from their vibrating tools such as grinders, drills and impact tools. Twenty-two workers decided not to have the audiometric test that was offered and therefore the study group with new audiometric data comprised 169 subjects.

The data abstracted from these workers' medical charts in 2008-9 included the age at assessment, years worked in construction, job title, audiometric test results and the HAVS Stockholm vascular scale results in each hand. This scale is based on the frequency and severity of cold-induced blanching in the fingers and ranges from 0 to 4 with stage 0 indicating no blanching and stage 4 the most severe abnormalities. (19) Audiometry had been carried out using a calibrated Tracor Instruments RA 410S micro-automated audiometer in a soundproof booth with measurement of hearing levels at 0.5, 1, 2, 3, 4, 6 and 8 kHz in each ear. The Workplace Safety and Insurance Board (WSIB) in Ontario uses a presbycusis-corrected average hearing level in the speech range (0.5 to 3 kHz) of 26.25 dB as the threshold for granting a pension for NIHL20 which is based on the American Medical Association Guides to the Evaluation of Permanent Impairment. (21) The presbycusis correction is (age in years - 60) x 0.5 for those over age 60 which is deducted from the average hearing level in the speech range to obtain the presbycusis-corrected average hearing level. Therefore this level of hearing loss was used in our study as the basis for identifying clinically significant hearing loss.

Statistical analyses were performed using SAS Version 9.2 (SAS Institute, Cary, NC). The continuous variables age, years worked in construction and many of the hearing levels at the specific audiometric frequencies were not normally distributed and therefore, in the bivariate analysis, Spearman rank correlations were used. The relationship between the number (%) of workers with a presbycusis-corrected hearing level [greater than or equal to]26.25 dB averaged over the speech range and years worked in construction in the categories <25, 25-40, >40 years was evaluated using the Cochran-Mantel-Haenszel test and treating the data as ordinal. To examine the effect of the HAVS Stockholm vascular scale on hearing loss, after controlling for years worked in construction, we first conducted multivariate (more than one dependent variable) linear regression with the hearing levels at all of the audiometric frequencies (0.5 to 8 kHz) as dependent variables and the HAVS Stockholm vascular scale and years worked in construction as independent variables. Follow-up univariate (single dependent variable) linear regressions were then conducted to examine whether hearing loss at each audiometric frequency was associated with the HAVS Stockholm vascular scale after controlling for years worked in construction. All of these regressions were carried out for each ear using the Stockholm vascular scale variable from the same side. Age could not be included in these models because it was highly correlated with years worked in construction. All p-values were two-tailed with p<0.05 being statistically significant.

The study was approved by the Research Ethics Board of St. Michael's Hospital, a teaching hospital affiliated with the University of Toronto.

RESULTS

All 169 workers in this study were men, median age of 57 (range: 28-75) and median years worked in construction of 35 (range: 4-52). One hundred and thirty-eight (81.7%) of the workers were pipefitters with the others working in similar trades. Of the 169 workers, 22 could not provide an accurate history of the frequency and distribution of finger blanching to allow the Stockholm vascular classification to be done. Of the 147 subjects who could be classified, the number (%) of subjects in the Stockholm scale stages is indicated in Table 1.

The audiometric hearing levels at each frequency in each ear are provided in Table 2. The highest mean hearing levels were obtained at 6 kHz in each ear and the highest median value of 40 dB was obtained at 4 kHz in the left ear and 6 kHz bilaterally. As indicated in Table 2, years worked in construction had statistically significant correlations (p<0.001) with the hearing levels at every audiometric frequency in each ear. The highest correlations were obtained at the audiometric frequencies of 6 kHz (r=0.47) for the right ear and 4 kHz (r=0.50) for the left ear.

The number (%) of subjects with a presbycusis-corrected average hearing level in the speech range >26.25 dB was 35 (20.7%) in the right ear, 48 (28.4%) in the left ear and 31 (18.3%) in both ears. As indicated in Table 3, there was a statistically significant increase (p<0.001) in the percentage of workers with this level of impairment for each ear and for both ears combined as the number of years in construction increased.

The results from the multivariate linear regression (Table 4) indicated that, after controlling for years worked in construction and hence noise exposure, the Stockholm vascular scale had a statistically significant effect on the audiometric hearing levels at all of the audiometric frequencies (0.5 to 8 kHz) for both the right side (F (7,138)=3.20, p=0.004) and the left side (F (7,138)=3.11, p=0.005). However, follow-up univariate linear regression analysis indicated that, after controlling for years worked in construction, the effect of the Stockholm vascular scale on the hearing level at each of the specific audiometric frequencies did not reach statistical significance except for 0.5 Hz on the left side.

DISCUSSION

In our study, there were statistically significant correlations between the hearing levels at each audiometric frequency and years worked in construction. The correlations were highest at 4 and 6 kHz and tapered off at 8 kHz, which is a typical pattern for NIHL. (1) Therefore the number of years worked in construction was probably a good metric for cumulative noise exposure in our study group. However, because of the high correlation between years worked in construction and age, it is likely that age also contributed to the hearing loss in some of the workers in our study.

This study found a high prevalence of clinically significant hearing loss in construction workers being assessed for HAVS. Thirty-one (18.3%) subjects had a presbycusis-corrected average hearing level in the speech frequencies of >26.25 dB in both ears, which is the level at which a pension would be granted for NIHL by the WSIB in Ontario. The proportion of subjects with this level of hearing loss increased as the number of years worked in construction increased, with the trend being statistically significant.

Other studies have found an increased risk of hearing loss in construction workers. Tak and Calvert (22) recently reported that the construction sector had the largest number of workers of any industrial sector in the US with hearing difficulty attributable to employment. The estimated prevalence (SE) of hearing difficulty in workers in the construction industry was 15.1% (0.5%) and the prevalence ratio (95% CI) in comparison to workers assumed not to be exposed to noise was 1.43 (1.31-1.57). Arndt et al. found a prevalence ratio of hearing loss of 1.5 (1.29-1.82) for construction workers in Germany in comparison to non-exposed controls. (23) Workers in Canada likely face similar risks of NIHL. Sinclair and Haflidson carried out a noise survey of workers in 27 construction projects and contractors' facilities in Ontario and found that the average noise exposure was 98.8 dB(A) with 91.3% of the samples exceeding 85 dB(A).4

Our study also found a statistically significant multivariate effect of the HAVS Stockholm vascular scale on the hearing levels at the audiometric frequencies 0.5 to 8 kHz after controlling for years worked in construction. However, the effect of HAVS on hearing appeared to be small because we could only identify a single audiometric frequency of the 14 specific frequencies tested that had a statistically significant association with the Stockholm vascular scale. Other studies have reported an association between VWF and hearing loss with the assumed mechanism being an increased susceptibility to generalized vasospasm, including vasospasm in the cochlea, in workers who develop HAVS.10-15 Interestingly, primary Raynaud's phenomenon unrelated to vibration exposure also has been found to be associated with increased susceptibility to NIHL. (10)

Zhu et al. reported greater temporary threshold shift in hearing from acute noise and hand-arm vibration exposure in comparison to just noise exposure in a small group of healthy subjects. (24) However, permanent hearing loss is the most important auditory outcome and this does not appear to be increased from combined noise and hand-arm vibration exposure in comparison to just noise exposure. (16) Our study included only workers exposed to hand-arm vibration and therefore could not further address this question.

Despite the fact that the hazardous auditory effects of noise have been known for many years, our study has indicated that construction workers continue to develop NIHL. An increased focus on prevention is needed for workers in this sector and should involve input from workers and employers and focus on all levels of prevention. (25) This would be aided by legislation restricting noise exposure, but in Ontario, the legislation which limits noise exposure to 85 dB(A) for an eight-hour daily exposure does not apply to con struction workers and there is no requirement for these workers to have routine audiometry. The situation is similar in the US in that the OSHA standard for noise exposure for construction workers is less rigorous than the standard for general industrial workers. (3,26) In addition, construction workers often move from one job site to another to carry out serial construction projects and this pattern of work is not conducive to having employers provide comprehensive surveillance as well as other program elements to prevent hearing loss. (3,26) It also creates difficulty for monitoring of programs by government inspectors. Construction contractors, workers, unions, health and safety associations and Ministries of Labour in Canada need to consider improved methods for prevention of NIHL in construction workers.

Received: October 21, 2009

Accepted: January 23, 2010

REFERENCES

(1.) Kurmis AP, Apps SA. Occupationally-acquired noise-induced hearing loss: A senseless workplace hazard. Int J Occup Med Environ Health 2007;20(2):127-36.

(2.) Nelson DI, Nelson RY, Concha-Barrientos M, Fingerhut M. The global burden of occupational noise-induced hearing loss. Am J Ind Med 2005;48(6):446 58.

(3.) Tak S, Davis RR, Calvert M. Exposure to hazardous workplace noise and use of hearing protection devices among US workers-NHANES, 1999-2004. Am J Ind Med 2009;52(5):358-71.

(4.) Sinclair JDN, Haflidson WO. Construction noise in Ontario. Appl Occup Environ Hyg 1995;10(5):457-60.

(5.) Hessel PA. Hearing loss among construction workers in Edmonton, Alberta, Canada. J Occup Environ Med 2000;42(1):57-63.

(6.) House RA, Pasut G. Evaluation of the audioscope in an industrial setting. J Occup Med 1992;34(5):539-45.

(7.) Griffin MJ, Bovenzi M. The diagnosis of disorders caused by hand-transmitted vibration: Southhampton Workshop 2000. Int Arch Occup Environ Health 2002;75(1-2):1-5.

(8.) Bovenzi M. Health risks from occupational exposures to mechanical vibration. Med Lav 2006;97(3):535-41.

(9.) Noel B. Pathophysiology and classification of the vibration white finger. Int Arch Occup Environ Health 2000;73(3):150-55.

(10.) Palmer KT, Griffin MJ, Syddall HE, Pannett B, Cooper C, Coggon D. Raynaud's phenomenon, vibration induced white finger, and difficulties in hearing. Occup Environ Med 2002;59(9):640-42.

(11.) Pyykko I, Starck J, Farkkila M, Hoikkala M, Korhonen O, Nurminen M. Handarm vibration in the aetiology of hearing loss in lumberjacks. Br J Ind Med 1981;38(3):281-89.

(12.) Pyykko I, Koskimies K, Starck J, Pekkarinen J, Farkkila M, Inaba R. Risk factors in the genesis of sensorineural hearing loss in forestry workers. Br J Ind Med 1989;46(7):439-46.

(13.) Iki M, Kurumatani N, Hirata K, Moriyama T. An association between Raynaud's phenomenon and hearing loss in forestry workers. Am Ind Hyg Assoc J 1985;46(9):509-13.

(14.) Miyakita T, Miura H, Futatsuka M. Noise-induced hearing loss in relation to vibration-induced white finger in chain-saw workers. Scand J Work Environ Health 1987;13(1):32-36.

(15.) Szanto C, Ligia S. Correlation between vibration induced white finger and hearing loss in miners. J Occup Health 1999;41(4):232-37.

(16.) Pyykko I, Pekkarinen J, Stark J. Sensory-neural hearing loss during combined noise and vibration exposure. Int Arch Occup Environ Health 1987;59(5):439 54.

(17.) Pekkarinen J. Noise, impulse noise, and other physical factors: Combined effects on hearing. Occup Med 1995;10(3):545-59.

(18.) House R. The effect of combined noise and vibration exposure on hearing. Occup Health Ont 1988;9(2):72-85.

(19.) Gemne G, Pyykko I, Taylor W, Pelmear PL. The Stockholm Workshop scale for the classification of cold-induced Raynaud's phenomenon in the hand-arm vibration syndrome (revision of the Taylor-Pelmear scale). Scand J Work Environ Health 1987;13(4):275-78.

(20.) Noise-induced Hearing Loss, On / After January 2, 1990. Document No. 1601-04. Toronto, ON: Workplace Safety and Insurance Board, 2008.

(21.) Guides to the Evaluation of Permanent Impairment, Third Edition (Revised). Milwaukee, WI: American Medical Association, 1990.

(22.) Tak S, Calvert GM. Hearing difficulty attributable to employment by industry and occupation: An analysis of the National Health Interview Survey United States, 1997 to 2003. J Occup Environ Health 2008;50(1):46-56.

(23.) Arndt V, Rothenbacher D, Brenner H, Fraisse E, Zschenderlein B, Daniel U, et al. Older workers in the construction industry: Results of routine health examination and a five year follow-up. Occup Environ Med 1996;53(10):686-91.

(24.) Zhu S, Sakakibara H, Yamada S. Combined effects of hand-arm vibration and noise on temporary threshold shifts of hearing in healthy subjects. Int Arch Occup Environ Health 1997;69(6):433-36.

(25.) Malchaire J, Piette A. A comprehensive strategy for the assessment of noise exposure and risk of hearing impairment. Ann Occup Hyg 1997;41(4):467-84.

(26.) Shuter AH. Construction noise: Exposure, effects and the potential for remediation; a review and analysis. Am Ind Hyg Assoc J 2002;63(6):768-89.

Ronald A. House, MD,CM, MSc, FRCPC, [1,2] John T. Sauve, BScH, [3] Depeng Jiang, PhD [4]

Author Affiliations

[1.] Division of Occupational and Environmental Health, Dalla Lana School of Public Health, University of Toronto, Toronto, ON

[2.] Department of Occupational and Environmental Health, St. Michael's Hospital, Toronto, ON

[3.] Medical student, University of Toronto, Toronto, ON

[4.] Keenan Research Centre, Li Ka Shing Knowledge Institute, St. Michael's Hospital, Toronto, ON

Correspondence: Dr. Ronald A. House, Department of Occupational and

Environmental Health, St. Michael's Hospital, 30 Bond St., Toronto, ON M5B 1W8, Tel: 416-864-5074, Fax: 416-864-5421, E-mail: houser@smh.toronto.on.ca

Conflict of Interest: None to declare.
Table 1. Number (%) of Subjects in the Stockholm Vascular
Scale Stages

Hand                   Stockholm Vascular Scale Stage *

             0            1            2            3          4

Right    28 (19.0%)   14 (9.5%)    51 (34.7%)   54 (36.7%)   0 (0%)
Left     28 (19.0%)   17 (11.6%)   48 (32.7%)   54 (36.7%)   0 (0%)

* The Stockholm scale stages as described by Gemne et al.19
are as follows:

Stage 0: No attacks of finger blanching

Stage 1: Occasional attacks affecting only the tips of one or
more fingers

Stage 2: Occasional attacks affecting distal and middle
(rarely also proximal) phalanges of one or more fingers

Stage 3: Frequent attacks affecting all phalanges of
most fingers

Stage 4: As in Stage 3, with trophic skin changes in
the fingertips

Table 2. Audiometric Hearing Levels and Spearman
Correlations with Years Worked in Construction

Ear     Frequency            Hearing Level           Correlation
          (kHz)      Mean (SD) *   Median (Range)     ([dagger])
                                                       (95% CI)

Right      0.5       18.4 (13.7)   15 (-10, 80)    0.16 (0.01-0.30)
                                                   ([double dagger])
            1        17.1 (13.9)   15 (0, 75)      0.24 (0.09-0.38)
            2        17.6 (16.2)   15 (-10, 90)    0.36 (0.22-0.48)
            3        27.4 (20.9)   25 (-5, 90)     0.43 (0.29-0.54)
            4        36.8 (21.5)   35 (-5, 90)     0.42 (0.28-0.53)
            6        40.9 (20.6)   40 (5, 90)      0.47 (0.34-0.58)
            8        35.5 (23.3)   30 (-5, 90)     0.42 (0.28-0.53)
Left       0.5       19.4 (15.1)   15 (0, 70)      0.22 (0.07-0.36)
            1        17.5 (15.6)   15 (-5, 80)     0.25 (0.10-0.38)
            2        20.1 (16.7)   20 (-5, 80)     0.34 (0.19-0.46)
            3        32.1 (20.8)   30 (-5, 90)     0.48 (0.35-0.59)
            4        40.4 (21.0)   40 (0, 90)      0.50 (0.37-0.60)
            6        43.7 (21.7)   40 (5, 90)      0.48 (0.36-0.59)
            8        37.8 (23.8)   35 (-10, 90)    0.45 (0.32-0.57)

* SD=Standard deviation.

([dagger]) Spearman correlation between audiometric hearing level
and years worked in construction.

([double dagger]) p<0.001 for all correlations.

Table 3. The Number (Percentage) of Workers with a
Presbycusis-corrected Average Hearing Level in the
Speech Range >26.25 dB According to Years Worked in
Construction

Ear       Mean HL *             Years Worked in Construction
        ([greater than
        or equal to]        <25          25-40           >40
            >26.25
Right        Yes          1 (3.7%)    13 (14.1%)      21 (42.0%)
              No         26 (96.3%)   79 (85.9%)      29 (58.0%)
Left         Yes          3 (11.1%)   19 (20.6%)      26 (52.0%)
              No         24 (88.9%)   73 (789.4%)     24 (48.0%)
Both         Yes          1 (3.7%)    11 (12.0%)      19 (38.0%)
              No         26 (96.3%)   81 (88.09%)     31 (62.0.0%)

Ear        p-value
          ([dagger])

Right       <0.001

Left        <0.001

Both        <0.001

* Mean HL=hearing level averaged over the speech range (0.5-3 kHz)
after subtracting a presbycusis correction for subjects aged over 60
years as follows: [(age in years - 60) x 0.5].

([dagger]) The p-value was obtained from the Cochran-Mantel-Haenszel
test treating the data as ordinal (i.e., indicative of trend).

Table 4. Linear Regression Analysis of Audiometric Hearing Levels

Ear     Audiometric    Predictor                      Estimate
         Frequency                                      (SE)

Right     Overall      Years in construction *
                       Stockholm vascular scale
                       ([dagger])

            0.5        Years in construction         0.37(0.12)
                       Stockholm vascular scale      1.08(1.07)

             1         Years in construction         0.47(0.12)
                       Stockholm vascular scale      0.80(1.07)

             2         Years in construction         0.58(0.14)
                       Stockholm vascular scale      2.03(0.19)

             3         Years in construction         1.03(0.17)
                       Stockholm vascular scale      1.18(1.47)

             4         Years in construction         1.02(0.17)
                       Stockholm vascular scale      1.27(1.54)

             6         Years in construction         1.05(0.17)
                       Stockholm vascular scale      1.50(1.46)

             8         Years in construction         1.02(0.19)
                       Stockholm vascular scale      0.71(1.70)

Left      Overall      Years in construction
                       Stockholm vascular scale

            0.5        Years in construction         0.49(0.13)
                       Stockholm vascular scale      2.32(1.14)

             1         Years in construction         0.55(0.13)
                       Stockholm vascular scale      1.12(1.17)

             2         Years in construction         0.72(0.14)
                       Stockholm vascular scale      0.58(1.20)

             3         Years in construction         1.16(0.16)
                       Stockholm vascular scale      0.17(1.38)

             4         Years in construction         1.27(0.16)
                       Stockholm vascular scale      1.97(1.37)

             6         Years in construction         1.11(0.16)
                       Stockholm vascular scale      0.50(1.44)

             8         Years in construction         1.11(0.19)
                       Stockholm vascular scale      1.68(1.62)

Ear     Audiometric    F-value   p-value
         Frequency

Right     Overall       6.81     <0.001
                        3.20      0.004

            0.5                   0.003
                                  0.31

             1                   <0.001
                                  0.46

             2                   <0.001
                                  0.09

             3                   <0.001
                                  0.42

             4                   <0.001
                                  0.41

             6                   <0.001
                                  0.30

             8                   <0.001
                                  0.68

Left      Overall       9.83     <0.001
                        3.11      0.005

            0.5                  <0.001
                                  0.04

             1                   <0.001
                                  0.34

             2                   <0.001
                                  0.63

             3                   <0.001
                                  0.90

             4                   <0.001
                                  0.15

             6                   <0.001
                                  0.73

             8                   <0.001
                                  0.30

* Years worked in construction is a continuous variable. The estimates
indicate the effect of a single year worked in construction.

([dagger]) Stockholm scale is treated as a continuous variable. The
estimates indicate the effect of one stage of the Stockholm scale.


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