OBJECTIVE: To evaluate whether long-term exposure to heavy environmental pollution with polychlorinated biphenyls (PCBs) could result in impairment of thyroid status as evaluated by an epidemiological field survey. METHODS: Thyroid volume (ThV) was measured by ultrasound in 238 employees of a factory (EMP) which previously produced PCBs and 454 adolescents from the surrounding area polluted by PCBs. Controls (C) were 572 adults and 965 adolescents from much less polluted areas. In the 238 EMP and various numbers (shown in parentheses) of adult C the levels of thyroid-stimulating hormone (TSH) (n = 498), thyroxine (n = 498), thyroglobulin (n = 278) and thyroid antibodies (anti-peroxidase (TPO Ab), n= 517; anti-thyroglobulin (Tg Ab), n=455; anti-TSH receptor (TSHR Ab), n=238) were estimated in serum, while only TSH and TPO Ab were measured in 269 and 171 adolescents from polluted and control areas respectively. In several subjects in whom thyroid disease was suspected, total tri-iodothyronine or free thyroxine and tri-iodothyronine were measured. In a total of 362 adults and adolescents the urinary iodine was estimated. RESULTS: Using the Mann-Whitney test, ThV in EMP (mean+/-S.E. = 18.85+/-0.69 ml, median= 17.3 ml, upper quartile=22.9 ml, n=238) was significantly higher (P< 0.001) than that in C (13.47+/-0.48 ml, 11.5 ml, 15.3 ml, n = 486 respectively). Similarly, ThV in adolescents from the polluted area (9.37+/-0.17 ml, 8.9 ml, 11.0 ml, n = 454 respectively) was significantly higher (P< 0.001) than that in C (8.07+/-0.10 ml, 7.6 ml, 9.6 ml, n = 965 respectively). In adults, a significantly increased prevalence of TPO Ab (P<0.05) was found (using the chi-square test) in EMP women of all ages (54/190) vs C women (70/282), in EMP women aged 31-50 years (40/117 vs 70/282 respectively) and those aged 41- 50 years (28/77 vs 54/215 respectively). Compared with C, there was also a higher prevalence of Tg Ab in EMP women aged 31-60 years (36/169 vs 50/342 respectively) and of TSHR Ab (P< 0.001) in the group of EMP men and women (25/238) vs sex- and age-matched C (6/238). No difference between EMP and C was found in the level of thyroxine (mean+/-S.D = 116.1+/-31.2 nmol/l, n = 238 vs 112.2+/-37.0 nmol/l, n = 460 respectively), TSH in the range 0.1-4.5 mU/l(1.56+/-0.86 mUl/l, n = 219 vs 1.51+/-0.84 mU/l, n = 460 respectively), prevalence of TSH >4.5 (14/238 vs 28/498 respectively) and <0.1 mU/l(5/238 vs 10/498 respectively). The prevalence of individuals without any defined clinical or laboratory signs of thyroid disorders among EMP who had worked in the factory for 21-35 years (43/128, 33.6%) was significantly lower than that in twice as many matched C (118/256, 46.1%, P< 0.025) or in EMP who had worked for only 11-20 years (36/73, 49.3%, P< 0.05). In adolescents, no difference was found in the prevalence of TPO Ab or TSH >4.5 mU/l between the polluted (17/269, 6.3%, and 2/243, 0.8% respectively) and C areas (15/171, 8.5% and 4/140, 2.8% respectively). The median values of urinary iodine were in the optimal range (microg per dl/number of cases) and about the same in polluted (12.6/90 and 11.4/55) and C areas (14.1/80, 13.2/82 and 13.4/55). CONCLUSIONS: Since iodine intake in Slovakia is considered sufficient as a result of 45 years of well-monitored iodine prophylaxis, the increased ThVand prevalence of thyroid disorders in the polluted areas presumably results from long-term exposure to toxic substances rather than from a difference in life-long iodine intake. The increased prevalence of some thyroid antibodies may be related to the known immunomodulatory effects of PCBs.
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