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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 %
Pryor et al. 1983 United States Authors surveyed 8 workers in municipal court office and 8 age and sex-matched controls in accounting office. 8 Unknown Unknown Eye, nasal, and throat complaints were higher in CCP exposed workers than in controls, but numbers were too small for meaningful comparison.
Olsen and Mørck 1985 Denmark Authors surveyed employees of 2 form-printing shops. 129 40 31 31% reported skin and mucous membrane symptoms; 22.5% reported skin symptoms only.
Omland et al. 1993 Denmark Authors surveyed 20 government office workers handling large amounts of CCP and a comparison group of 20. 20 10 50 Increased incidences of pruritus (P=0.007) and skin irritation (P=0.03) were associated with CCP. A dose-response relationship was established between pruritus and increased handling of CCP (P=0.049).
Apol and Thoburn 1986 United States Authors surveyed 65 employees making CCP. Ambient evaluation was also performed. 65 Unknown No numbers were presented. Maintenance workers in the coater area reported the most problems; 4 men reported pulmonary symptoms consistent with exposure to diisocyanates.
  1. The number of CCP-exposed workers surveyed was not generally known except for those responding to the surveys; therefore, response rates were unknown.
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