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.
Langer
P
P
Institute of Experimental Endocrinology, Slovak Academy of Science, Bratislava, Slovakia. pavel.langer@savba.sk
Tajtaková
M
M
Kocan
A
A
Vlcek
M
M
Petrik
J
J
Chovancova
J
J
Drobna
B
B
Jursa
S
S
Pavuk
M
M
Trnovec
T
T
Sebokova
E
E
Klimes
I
I
D000328:Adult; D000368:Aged; D002617:Chemical Industry; D003633:Dichlorodiphenyl Dichloroethylene / Q000097:blood; D004787:Environmental Pollution; D005260:Female; D006581:Hexachlorobenzene / Q000097:blood; D006801:Humans; D006843:Hydrocarbons, Chlorinated / Q000097:blood*; D007306:Insecticides / Q000097:blood; D008297:Male; D008875:Middle Aged; D009784:Occupational Diseases / Q000097:blood; D009929:Organ Size; D010865:Pilot Projects; D011078:Polychlorinated Biphenyls / Q000097:blood; D013961:Thyroid Gland / Q000000981:diagnostic imaging* / Q000473:pathology; D013972:Thyrotropin / Q000097:blood; D014463:Ultrasonography
D006843:Hydrocarbons, Chlorinated; D007306:Insecticides; D003633:Dichlorodiphenyl Dichloroethylene; D006581:Hexachlorobenzene; D013972:Thyrotropin; D011078:Polychlorinated Biphenyls