Clark v. Burlington Industries, Inc.

338 S.E.2d 553, 78 N.C. App. 695, 1986 N.C. App. LEXIS 2006
CourtCourt of Appeals of North Carolina
DecidedJanuary 21, 1986
Docket8510IC449
StatusPublished
Cited by11 cases

This text of 338 S.E.2d 553 (Clark v. Burlington Industries, Inc.) is published on Counsel Stack Legal Research, covering Court of Appeals of North Carolina primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Clark v. Burlington Industries, Inc., 338 S.E.2d 553, 78 N.C. App. 695, 1986 N.C. App. LEXIS 2006 (N.C. Ct. App. 1986).

Opinion

EAGLES, Judge.

Plaintiff worked for defendant Burlington Industries from 1951 to 1976, and from 1979 to his retirement in 1983. He worked in Burlington’s “weave rooms,” where power looms made continuous noise at or above the 90 decibel (db) level. (During the period 1976-1979 plaintiff worked in home maintenance and was not exposed to loud mechanical noise.) On 1 October 1971, new provisions of the Workers’ Compensation Act went into effect which allowed compensation for occupational hearing loss related to long-term exposure to harmful noise. Shortly thereafter, Burlington issued hearing protective devices and began a program of regular testing. Plaintiff was identified by Burlington as a hearing problem case.

In February 1983, plaintiff filed this claim. The medical testimony indicated that plaintiff had in fact suffered substantial hearing loss resulting from exposure to loud noise in Burlington’s plants. Plaintiff suffered the great majority of this hearing loss prior to 1 October 1971, but he also suffered some slight loss after that time. This later loss, according to the medical expert, could not be definitively traced to a single cause.

Deputy Commissioner Shuping denied compensation, finding that the loss of hearing after 1971 was due either to variations in audiometric testing equipment or to aging, and that there was no occupationally caused increase, however slight, in the loss of hearing existing as of 1 October 1971. Deputy Commissioner Shuping ruled in effect that upon being provided hearing protection devices by Burlington, plaintiff was removed from exposure to harmful noise. Accordingly, plaintiff could not and did not suffer further injurious exposure. The only time period in which injurious exposure could have occurred after 1 October 1971 was 1 October (effective date of Act) to 11 October 1971 (date of provi *697 sion of protective devices), and this exposure did not contribute to plaintiffs hearing loss.

On appeal by plaintiff, the full Commission affirmed denial of compensation, with Commissioner Clay dissenting. The Commission’s majority opinion stated that the provisions of G.S. 97-53(28) allowed no compensation for hearing loss existing prior to the Act’s effective date, and that the ear protection equipment issued by Burlington reduced the noise level in plaintiffs ears below 90db beginning in 1972. On that logic, the majority adopted and affirmed Deputy Commissioner Shuping’s opinion and award.

Commissioner Clay wrote in his dissent that plaintiff had in fact suffered compensable loss of hearing, since (1) there was evidence he suffered some loss of hearing after 1 October 1971, (2) the hearing protection devices failed to actually remove plaintiff from exposure to harmful noise and (3) compensation for hearing loss occurring before 1 October 1971 would be compensable, provided there was some loss after the date. From the decision of the full Commission, plaintiff appealed.

I

Our review of decisions of the Industrial Commission is limited in scope, and usually this court determines solely whether there is any competent evidence to support the Commission’s findings and whether these in turn support the Commission’s conclusions of law. Where, however, the Commission finds facts or fails to find sufficient facts while acting under a misapprehension of law, it is sometimes necessary to remand the case so that the evidence may be considered by the Commission in its true legal light. Mills v. Fieldcrest Mills, 68 N.C. App. 151, 314 S.E. 2d 833 (1984). We find that to be the case here and accordingly remand.

II

The full Commission found as grounds for denying compensation that the noise in plaintiffs ears was reduced below 90db by the provision and use of protective devices. The Commission relied on G.S. 97-53(28)a, which establishes a conclusive presumption that exposure to noise of less than 90db is not harmful. McCuiston v. Addressograph-Multigraph Corp., 308 N.C. 665, 303 S.E. 2d 795 (1983). The 90db level is consistent with federal maximum permissible noise exposure levels. Id.; see 29 C.F.R. 1910.95 (1982). *698 The federal noise protection regulations have been adopted by reference by the North Carolina Department of Labor, 13 N.C.A.C. 7C.0101(a)(18) (1985). However the federal regulations do not allow permissible noise exposure levels to be measured in the ear. The federal regulatory structure relies on engineering and administrative controls to reduce workplace noise; individual protective devices may be used only in a supplementary role. See 46 Fed. Reg. 4078 (1981). Although the federal OSHA has questioned the economic and technological feasibility of this regulatory approach, it remains in effect. Id. Federal, hence North Carolina, industrial noise monitoring requirements require noise to be measured in the workplace. We may not rely merely on what level of noise may reach an employee’s ear. The original noise protection rule did require individual monitoring for high risk employees, but even there the microphone was to be placed not at the eardrum, but instead not less than two inches nor more than two feet from the employee’s ear. 29 C.F.R. 1910.95(g)(2)(ii)(D) (1982) (stayed pending further rulemaking). Rather than focus monitoring on exposure at the ear, federal OSHA, in response to industry pressure, now relies on required area monitoring. 46 Fed. Reg. 42622, 42623-24 (1981). Employer contentions that compliance with the 90db standard should be measured inside the hearing protective device, rather than in the workplace, have been rejected. The federal Occupational Safety and Health Review Commission has insisted instead that ambient noise first be reduced to the lowest feasible level. In re Flxible Corp., 12 O.S.H.C. 1053 (1984) (rejecting contention that noise should be measured inside helmet); In re Turner Co., 4 O.S.H.C. 1554 (1976) (plain language of regulations sufficed to summarily reject contention).

While the Industrial Commission’s interpretation of G.S. 97-53(28) is entitled to due consideration, the final say rests with the courts. In re Broad and Gales Creek Community Assoc., 300 N.C. 267, 266 S.E. 2d 645 (1980). In determining the legislative intent and interpreting the statute, we consider inter alia the historical reasons for the statute’s enactment and its relationship and interplay with other statutes and regulations. See Carolinas-Virginias Assoc. of Bldg. Owners and Managers v. Ingram, 39 N.C. App. 688, 251 S.E. 2d 910, disc. rev. denied, 297 N.C. 299, 254 S.E. 2d 925 (1979). In light of the regulatory framework discussed above, *699 we hold that the 90db limit in G.S. 97-53(28) is the ambient noise level, and that the Commission accordingly acted under a misapprehension of law in ruling otherwise.

Ill

It appears that the Commission may have drawn its interpretation from G.S. 97-53(28)i, upon which Deputy Commissioner Shuping relied. That section reads in full:

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338 S.E.2d 553, 78 N.C. App. 695, 1986 N.C. App. LEXIS 2006, Counsel Stack Legal Research, https://law.counselstack.com/opinion/clark-v-burlington-industries-inc-ncctapp-1986.