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4 HEALTH EFFECTS

Table 4–3(Continued). Summary of cross-sectional studies that used questionnaires to assess the health effects of indoor air contaminants in general or CCP specifically
Study Country Methods CCP-exposed workers Results
Number responding to survey[1] Workers with complaints
Number %
Göthe et al. 1981 and Norbäck et al. 1983b Sweden Authors described complaints from handling CCP, ordinary bond paper, or carbon paper; used a comparison group of 22. Unknown 58 Unknown The prevalence of mucous membrane symptoms (P<0.01) was greater with CCP than with ordinary bond or carbon paper.
Kolmodin-Hedman et al. 1981 Sweden Authors surveyed the following: Laboratory workers handled >1,000 CCP sheets/day compared with insurance workers handling fewer sheets (unspecified no.) and office controls who handled no CCP. Symptom prevalence: 92%, 32%, and 10%, respectively.
Insurance workers 145 46 32
Hospital laboratory workers 12 11 92
Hospital office workers (controls) 20 2 10
Kleinman and Horstman 1982 United States Authors surveyed workers in 61 U. of Washington offices with heavy CCP use. Subjects were asked about symptoms caused by CCP; respondents had a physical examination. 265 71 27 Significant dose-response relationship reported between CCP use and health complaints. Estimated minimum rate of complaints across different offices was 11%.

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See footnotes at end of table.

(Continued)
Carbonless Copy Paper
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  1. The number of CCP-exposed workers surveyed was not generally known except for those responding to the surveys; therefore, response rates were unknown.