Ototoxicity.The January 2005 issue of EHP EHP abbr. 1. effective horsepower 2. electric horsepower provided a much-needed overview of the prevalence of environment noise and its effects on health (Chepesiuk 2005; Manuel 2005; Schmidt 2005). Indeed, noise is pervasive and its adverse health effects are among the most common occupational injuries. Your consideration of noise-induced damage is especially welcome, given the strong focus of EHP on overexposure overexposure too long an exposure time or too high a milliamperage causing too black a picture, loss of detail and some anomalies of translucency. to chemical agents relative to overexposure to physical stimuli. Curiously absent from the discussion, however, was a review of the evidence that has accumulated over the past two decades concerning the ability of chemical agents to produce hearing impairment directly (ototoxicity Ototoxicity Definition Ototoxicity is damage to the hearing or balance functions of the ear by drugs or chemicals. Description Ototoxicity is drug or chemical damage to the inner ear. ) and to interact with noise exposure yielding either additive or synergistic impairment of the auditory apparatus. Research on such processes has received support in the United States from multiple agencies, including the National Institute of Environmental Health Sciences The National Institute of Environmental Health Sciences (NIEHS) is one of 27 Institutes and Centers of the National Institutes of Health (NIH),which is a component of the Department of Health and Human Services (DHHS). The Director of the NIEHS is Dr. David A. Schwartz. , the National Institute for Deafness and Other Communication Disorders, the National Institute for Occupational Safety and Health National Institute for Occupational Safety and Health, n.pr an institute of the Centers for Disease Control and Prevention that is responsible for assuring safe and healthful working conditions and for developing standards of safety and health. , and the U.S. Environmental Protection Agency Environmental Protection Agency (EPA), independent agency of the U.S. government, with headquarters in Washington, D.C. It was established in 1970 to reduce and control air and water pollution, noise pollution, and radiation and to ensure the safe handling and . Occupational epidemiology studies have demonstrated noise-chemical interactions in the workplace, and laboratory animal models have been effective in identifying ototoxicants, establishing dosimetry dosimetry /do·sim·e·try/ (do-sim´e-tre) scientific determination of amount, rate, and distribution of radiation emitted from a source of ionizing radiation, in biological d. , identifying targets of toxicity, and determining the mechanisms for such ototoxicity. For example, occupational epidemiologic studies of Morata et al. (1997) demonstrated an excess risk of developing hearing loss among workers exposed to mixed solvents (mainly toluene toluene (tōl`y ēn') or methylbenzene (mĕth'əlbĕn`zēn), C7H8 ) plus noise among printers compared with noise-exposed referent subjects or non-exposed matched controls. Similar studies have subsequently been published for styrene-exposed workers in the reinforced plastic industry (Morata et al. 2002; Sliwinska-Kowalska et al. 2003). In laboratory animals, the pioneer experiments on the ototoxicity of solvents were initiated by Pryor and Rebert in the 1980s (e.g., Pryor et al. 1987; Rebert et al. 1983). Since these early studies, the ability of chemicals to directly disrupt auditory function has been established for trichloroethylene trichloroethylene /tri·chlo·ro·eth·y·lene/ (-eth´i-len) a clear, mobile liquid used as an industrial solvent; formerly used as an inhalant anesthetic. tri·chlo·ro·eth·yl·ene n. (Crofton et al. 1993; Fechter et al. 1998), toluene (Campo et al. 1999; Crofton et al. 1994; Johnson 1993), ethyl benzene (Cappaert et al. 2001), and styrene (Campo et al. 2001), among other agents. In addition, Lataye et al. (2001, 2003) have nicely identified the route by which solvents enter the cochlea cochlea (kŏk`lēə): see ear. and the pattern of damage that they produce in the inner ear. Using developmental models, Rice and Gilbert (1992) demonstrated that methyl mercury exposure could impair auditory function in young primates. Also, hearing impairments have been reported for lead-exposed children (Osman et al. 1999; Schwartz and Otto 1987, 1991). Crofton and colleagues (Crofton et al. 1999, 2000; Lasky et al. 2002) demonstrated the ability of polychlorinated biphenyls to disrupt the development of the cochlea in rats by disrupting thyroid function. In this laboratory, we have demonstrated that a series of chemical contaminants with potential to disrupt intrinsic antioxidant pathways or to enhance reactive oxygen species reactive oxygen species, n molecules and ions of oxygen that have an unpaired electron, thus rendering them extremely reactive. Many cellular structures are susceptible to attack by ROS contributing to cancer, heart disease, and cerebrovascular disease. (ROS ROS, n.pr See reactive oxygen species. ) generation can produce permanent hearing loss in the presence of noise. These agents include carbon monoxide (Fechter et al. 1987, 1988, 2000), hydrogen cyanide (Fechter et al. 2002), and acrylonitrile (Fechter et al. 2003; Pouyatos et al. 2005). This research provided evidence that intense noise can initiate ROS generation, resulting in cochlear cochlear pertaining to or emanating from the cochlea. cochlear duct the coiled portion of the membranous labyrinth located inside the cochlea; contains endolymph. cochlear nerve see Table 14. damage. We hypothesized that even moderate noise levels, including noise close to permissible workplace exposure levels, may initiate ROS formation but that these are normally contained by antioxidant pathways. However, in the presence of pro-oxidant chemical agents, we demonstrated that even mild noise can yield oxidative stress leading to the death of sensory receptor cells for sound, the outer hair cells, and subsequent permanent impairment of auditory function (Fechter et al. 2000, 2002, 2003; Pouyatos et al. 2005). It is striking, although not surprising, that the auditory system is vulnerable to a range of chemical agents that initiate toxic processes that have been more fully studied in the brain and other organ systems. The existing evidence has clear implications for both environmental and occupational health, and it highlights the continuing need for research on the issue. In Europe, the scientific information available has influenced public health policy. In February 2003, the European Parliament and the Council of the European Union Council of the European Union, branch of the governing body of the European Union (EU) that has the final vote on legislation proposed by the European Commission and deliberated by the European Parliament. (2003) published Directive 2003/10/EC on minimum safety requirements regarding the exposure of workers to noise. Ultimately, an increase in the awareness of the ototoxic ototoxic /oto·tox·ic/ (o´to-tok?sik) having a deleterious effect upon the eighth nerve or on the organs of hearing and balance. o·to·tox·ic adj. potential of chemicals should improve preventive efforts and help reduce the risk of hearing loss. The authors declare they have no competing financial interests. Laurence D. Fechter Benoit Pouyatos Loma Linda VA Medical Center Loma Linda, California Loma Linda is a city in San Bernardino County, California, United States. The population was 18,681 at the 2000 census. Geography Loma Linda is located at (34.048364, -117.250648)GR1. E-mail: Larry.fechter@med.va.gov REFERENCES Campo P, Lataye R, Loquet G, Bonnet P. 2001. Styrene-induced hearing loss: a membrane insult. Hear Res 154(1-2):170-180. Campo P, Loquet G, Blachere V, Reure M. 1999. Toluene and styrene intoxication route in the rat cochlea. Neurotoxicol Teratol 21(4):427-434. Cappaert NL, Klis SF, Muijser H, Kulig BM, Smoorenburg GF. 2001. Simultaneous exposure to ethyl benzene and noise: synergistic effects on outer hair cells. Hear Res 162(12):67-79. Chepesiuk R. 2005. Decibel decibel (dĕs`əbĕl', –bəl), abbr. dB, unit used to measure the loudness of sound. It is one tenth of a bel (named for A. G. Bell), but the larger unit is rarely used. hell: the effects of living in a noisy world. Environ Health Perspect 113:A35-A41. Crofton KM, Ding D, Padich R, Taylor M, Henderson D. 2000. Hearing loss following exposure during development to polychlorinated biphenyls: a cochlear site of action. Hear Res 144(1-2):196-204. Crofton KM, Rebert CS, Lassiter TL. 1994. Solvent-induced ototoxicity in rats: an atypical selective mid-frequency hearing deficit. Hear Res (80):25-30. Crofton KM, Rice DC. 1999. Low-frequency hearing loss following perinatal exposure to 3,3',4,4',5-pentachlerobiphenyl (PCB PCB: see polychlorinated biphenyl. PCB in full polychlorinated biphenyl Any of a class of highly stable organic compounds prepared by the reaction of chlorine with biphenyl, a two-ring compound. 126) in rats. Neurotoxicol Teratol 21(3):299-301. Crofton KM, Zhao X. 1993. Mid-frequency hearing loss in rats following inhalation exposure to trichloroethylene: evidence from reflex modification audiometry. Neurotoxicol Teratol 15(6):413-423. European Parliament and the Council of the European Union. 2003. Directive 2003/10/EC of the European Parliament and the Council of 6 February 2003 on the Minimum Health and Safety Requirements Regarding the Exposure of Workers to the Risks Arising from Physical Agents (Noise). Available: http://europa.eu.int/eur-lex/pri/en/oj/ dat/2003/1_042/1_04220030215en00380044.pdf [accessed 27 May 2005]. Fechter LD, Chen GD, Johnson DL. 2002. Potentiation potentiation /po·ten·ti·a·tion/ (po-ten?she-a´shun) 1. enhancement of one agent by another so that the combined effect is greater than the sum of the effects of each one alone. 2. posttetanic p. of noise-induced hearing loss noise-induced hearing loss Temporary or permanent hearing loss caused either by a single exposure to very loud sound(s) or by repeated exposure to louder sounds over an extended period. See Hearing loss. by low concentrations of hydrogen cyanide in rats. Toxicol Sci 66(1):131-138. Fechter LD, Chen GD, Rao D, Larabee J. 2000. Predicting exposure conditions that facilitate the potentiation of noise-induced hearing loss by carbon monoxide. Toxicol Sci 58(2):315-323. Fechter LD, Klis SFL SFL - System Function Language. Assembly language for the ICL2900. "SFL Language Definition Manual", TR 6413, Intl Computers Ltd. , Shirwany NA, Moore TG, Rao D. 2003. Acrylonitrile produces transient cochlear function loss and potentiates permanent noise-induced hearing loss. Toxicol Sci 75(1):117-123 Fechter LD, Liu Y, Herr DW, Crofton KM. 1998. Trichloro-ethylene ototoxicity: evidence for a cochlear origin. Toxicol Sci 42(1):28-35. Fechter LD, Thorne PR, Nuttall AL. 1987. Effects of carbon monoxide on cochlear electrophysiology and blood flow. Hear Res 27(1):37-45. Fechter LD, Young JS, Carlisle L. 1988. Potentiation of noise induced threshold shifts and hair cell loss by carbon monoxide. Hear Res 34(1):39-47. Johnson AC. 1993. The ototoxic effect of toluene and the influence of noise, acetyl acetyl /ac·e·tyl/ (as´e-til) (as´e-tel?) (ah-se´til) the monovalent radical CH3COsbond, a combining form of acetic acid. a·ce·tyl n. salicylic acid, or genotype. A study in rats and mice. Scand Audiol Suppl 39:1-40. Lataye R, Campo P, Barthelemy C, Loquet G, Bonnet P. 2001. Cochlear pathology induced by styrene. Neurotoxicol Teratol 23(1):71-79. Lataye R, Campo P, Pouyates B, Cossec B, Blachere V, Morel G. 2003. Solvent etotoxicity in the rat and guinea pig. Neurotoxicol Teratol 25(1):39-50. Lasky RE, Widholm JJ, Crofton KM, Schantz SL. 2002. Perinatal exposure to Aroclor 1254 impairs distortion product otoacoustic emissions (DPOAEs) in rats. Toxicol Sci 68(2):458-404. Manuel J. 2005. Clamoring for quiet: new ways to mitigate noise. Environ Health Perspect 113:A47-A49. Morata TC, Johnson AC, Nylen P, Svensson EB, Cheng J, Krieg EF, et al. 2002. Audiemetric findings in workers exposed to low levels of styrene and noise. J Occup Environ Med 44(9):806-814. Morata TC, Fiorini AC, Fischer EM, Colacioppo S, Wallingford KMM KMM Keyboard/Monitor/Mouse KMM Keep Middlesex Moving (New Brunswick, NJ) KMM Kitco Minerals and Metals KMM K-Meleon Macro KMM Knowledge Management and Marketing KMM Key Management Message , Krieg EE, et el. 1997. Toluene-induced hearing loss among rotogravure rotogravure: see printing. printing workers. Scand J Work Environ Health 23(4):289-298. Pouyatos B, Gearhart C, Fechter LD. 2005. Acrylonitrile potentiates hearing loss and cochlear damage induced by moderate noise exposure in rats. Toxicol Appl Pharmacol 204(1):46-56. Osman K, Pawlas K, Schutz A, Gazdzik M, Sokat JA, Vahter M. 1999. Lead exposure and hearing effects in children in Katowice, Poland. Environ Res 80(1):1-8. Pryor GT, Rebert CS, Howd RA. 1987. Hearing loss in rats caused by inhalation of mixed xylenes and styrene. J Appl Toxicol 7(1):55-61. Rebert CS, Sorenson SS, Howd RA, Pryor GT. 1983. Toluene-induced hearing loss in rats evidenced by the brainstem auditory-evoked response. Neurobehav Toxicol Teratol 5(1):59-62. Rice DC, Gilbert SG. 1992. Exposure to methyl mercury from birth to adulthood impairs high-frequency hearing in monkeys. Toxicol Appl Pharmacol 115(1):6-10. Schmidt CW. 2005. Noise that annoys: regulating unwanted sound. Environ Health Perspect 113:A43-A44. Sliwinska-Kowalska M, Zamyslowska-Szmytke E, Szymezak W, Kotylo P, Fiszer M, Wesolowski W, et al. 2003. Ototoxic effects of occupational exposure to styrene and co-exposure to styrene and noise. J Occup Environ Med 45(1):15-24. Schwartz J, Otto D. 1987. Blood lead, hearing thresholds, and neurobehavioral development in children and youth. Arch Environ Health 420(3):153-160. Schwartz J, Otto D. 1991. Lead and minor hearing impairment. Arch Environ Health46(5):300-305. |
|
||||||||||||||||

ēn')
Printer friendly
Cite/link
Email
Feedback
Reader Opinion