Multiple organochlorine pollution and the thyroid.

OBJECTIVE: Although the biological effects of major persistent organochlorinated pollutants (POPs) appear to be essentially similar, some effects which would be specific for certain substance cannot be excluded. We attempted to study the thyroid volume and thyrotropin level in the population living in the area with multiple pollution by polychlorinated biphenyls (PCBs) and pesticides (DDE and hexachlorobenzene - HCB). METHODS: A total of 454 adults was examined within the pilot field survey in 1998. Among them were 237 males (age range 19-78 years, median 47) and 227 females (age range 19-78 years, median 48). Fifteen environmentally prevalent congeners of polychlorinated biphenyls and also p,p-DDE (2,2-bis(4-chlorophenyl)-1,1-dichloroethylene), p,p-DDT (2,2-bis(4-chlorophenyl)- 1,1,1-trichloro-ethane), hexachlorobenzene (HCB) as well as alpha-, beta- and gamma-hexachlorocyclohexane (HCH) were determined in serum by high resolution gas chromatography using microelectron capture detector and microcapillary column. Thyroid volume (ThV) was measured by real time sonography using the ellipsoid method with the aid of sonographic instrument Sonoline SI-400 (Siemens, Germany). The level of TSH was estimated by supersensitive immunoradiometric method using commercial kits by Immunotech (Marseille, France). Pearsons correlation coefficients after logarithmic transformation of values and Spearmans correlation coefficients were used for statistical evaluation. RESULTS: Significant positive association (p<0.01) was found between DDE and PCB, DDE and HCB, while that between PCB and HCB was not significant. Similar positive association (p<0.01) was also found between each individual organochlorine and their sum. Significant negative association (p<0.01) was found between ThV and TSH. When using categorical PCB values either >2000 (N=208) or >3000 (N=127) ng/g lipid, significant positive association (p<0.05 and p<0.01, respectively) was found between the sum of all organochlorines (PCB+DDE+HCB) and ThV, while that between PCB and ThV (p<0.01) was found only at the PCB levels >3000 ng/g lipid. When using Spearmans correlation coefficients, significant negative association appeared between PCB and TSH (p<0.05), sum of organochlorines and TSH (p<0.05) and ThV and TSH (p<0.01). CONCLUSIONS: Although several significant positive and negative associations were found, this study, like several others, could not exactly define the participation level of individual POPs in their common toxic effects, but possibly contributed to the recognition and elucidation of some problems related to this task.

Human thyroid in the population exposed to high environmental pollution by organochlorinated pollutants for several decades.

OBJECTIVE: To study possible effects of long-time exposure of chemical factory employees and population of surrounding polluted area to polychlorinated biphenyls and pesticides on the thyroid volume and function as compared to the population from the area of background pollution. METHODS: A total of 461 adults consisting of 239 men and 222 women was examined and divided into four groups according to their permanent domicile as related to the level of environmental pollution, e.g. SR (area of background pollution, n = 207), SI (slightly polluted area, n = 59), MI (polluted city of Michalovce, n = 94) and CH (employees of chemical factory subjected to high PCB exposure, n = 101), combined first three groups being also called LPA (less polluted areas, n = 360). Thyroid volume (ThV) and echogenicity were measured by real time sonography. The level of polychlorinated biphenyls (PCB) and pesticides (hexachlorbenzene--HCB, DDE (2,2'-2-bis(4-chlorobiphenyl)- 1,1-dichloroethylene), p,p'-DDT (2,2'-bis(4-chlorophenyl)- 1,1,1-trichloroethane) and alpha-, beta- and gamma-hexachlorcyclohexane--HCH) was estimated by congener specific analysis using HP 5890 gas chromatograph with a 63Ni electron capture detector. Serum levels of thyrotropin (TSH) and thyroid peroxidase antibodies (anti-TPO) were measured by specific sensitive immunoassays. RESULTS: The association of very high PCB level (e.g. 7300 +/- 871 ng/g lipid; mean +/- S.E.) with increased ThV (e.g. 16.3 +/- 0.73 ml) in CH has been found, the values being significantly higher than these of 360 subjects in LPA (e.g. 2045 +/- 147 ng/g, p < 0.001 for PCB and 14.0 +/- 0.32 ml, p < 0.001 for ThV). In 23 subjects from CH with PCB level > 10000 ng/g the ThV was 18.7 +/- 2.32 ml, while that in 251 subjects from LPA with PCB level of < 2000 ng/g was 13.8 +/- 0.35 ml (p < 0.05). In addition, ThV as well as PCB levels were strikingly increasing with age. In parallel with PCB levels, also the levels of other organochlorines estimated (namely these of DDE) were increasing. Although the participation of these substances in the development of adverse effects cannot yet be defined, it cannot be excluded. The association of increased levels of episodic congener PCB 101 with increased ThV appeared to be more pronounced than that of stable congeners PCB 153 and 180. Finally, significant increase in the frequency of thyroid hypoechogenicity by ultrasound, ThV > 20.0 ml and thyroperoxidase antibodies in CH area was observed as compared to LPA. CONCLUSIONS: Several associations of high PCB and pesticides level with characteristics of thyroid disorders (e.g. increased thyroid volume, frequency of hypoechogenicity and frequency of positive thyroperoxidase antibodies level in blood) were observed in the area with heavy industrial pollution by PCB.

Atmospheric mercury levels in the Slovak Republic.

Total mercury concentrations (as a sum of vapor and particulate mercury) were measured in 24-h samples of ambient air in 20 different localities of the Slovak Republic eight times during the period 1996-1997. Vapor mercury was analyzed on site by atomic fluorescence with amalgamation technique. Particulate mercury was determined by vapor hydride atomic absorption spectrometry after wet digestion of filters with particulate air samples. The results showed that 34% of the 160 individual total mercury concentrations exceeded 5 ng/m3--the ambient air quality guideline value recommended by the WHO. The range of total mercury concentrations in the ambient air of Slovakia was: 1.13-3.98 ng/m3 (geom. mean 2.63) in the background area; 2.25-5.27 ng/m3 (geom. mean 3.64) in the agricultural areas; 1.73-20.53 ng/m3 (geom. mean 4.57) in the urban areas; and 1.53-39.85 ng/m3 (geom. mean 5.28) in the industrial areas. The highest mercury levels occurred in areas with metallurgical industry and coal combustion. The predominant form of mercury present in air was vapor mercury. The particulate fraction of mercury in ambient air (as a percentage of total mercury) varied widely from 0.4% to 42.1% (geom. mean = 4.4%). This fraction was lower in agricultural areas (2.3%) than in urban areas (5.3%). Although the atmospheric vapor mercury concentrations were slightly higher in summer than in winter, a direct correlation of vapor mercury concentrations and ambient air temperature was not found. Furthermore, the particulate mercury concentrations did not correlate with total particulate levels.

Environmental contamination with polychlorinated biphenyls in the area of their former manufacture in Slovakia.

Evidently increased environmental pollution as a consequence of the 25-year manufacture of polychlorinated biphenyls (PCBs) in eastern Slovakia was observed. PCB levels determined in ambient air, soil, surface water, bottom sediment, wildlife (fish and game) samples collected in a potentially contaminated area of about 250 km2 (a part of the Michalovce district) were compared with those determined in a control area (Stropkov district). Up to 1700 ng/m3 were found in ambient air in a village close to a manufacturer's dumping site and a highly contaminated manufacturer's effluent canal whereas PCB concentrations in ambient air samples taken in villages in the control area were about 80 ng/m3 only. While soil samples taken from the agricultural fields of the polluted area contained PCBs at levels comparable with soil samples from the control area (about 0.008 mg/kg) much higher values (from 0.4 to 53,000 mg/kg) were determined in soil taken in the vicinity of manufacturer's landfill and storage sites and especially plants preparing asphalted gravel using formerly PCBs in their heat-exchanging systems. The contamination of the Laborec river and large Zemplinska Sirava reservoir is caused by the manufacturer's effluent canal since PCB levels in the canal sediment are still to be found about 3000 mg/kg. While PCB levels in sediment samples from Michalovce watercourses ranged between 1.7 and 6 mg/kg, sediment samples from the control Stropkov district ranged between 0.007 and 0.052 mg/kg only. Fish living in contaminated Michalovce waters contained about hundred times higher PCB levels than those caught in Stropkov ones. Similarly, game animals shot in Michalovce forests contained several times higher levels than those shot in Stropkov ones.