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Organohalogen concentrations and a gross and histologic ...

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Dioxin-like contaminants<br />

Extraction <strong>and</strong> analyses of 2,3,7,8-tetrachlorodibenzo-p-dioxin (2,3,7,8-<br />

TCDD) <strong>and</strong> non-ortho PCB congener 3,3’,4,4’,5-pentachlorobiphenyl (CB-126)<br />

in polar bear fat was conducted by Axys Analytical Services (Sidney, BC,<br />

Canada) used previously described techniques with only minor modification<br />

(U.S. EPA, 1998, 1999). 2,3,7,8-TCDD <strong>and</strong> CB-126 were chosen as<br />

model dioxin-like contaminants since the former is the most potent AhR<br />

agonist among all dioxin <strong>and</strong> furan congeners, <strong>and</strong> CB-126 is the most potent<br />

AhR agonist among all PCB congeners. Briefly, fat samples were homogenized<br />

with Na 2 SO 4 <strong>and</strong> spiked with mixture of 13 C-labelled non-ortho<br />

PCBs <strong>and</strong> 2,3,7,8-TCDD surrogate st<strong>and</strong>ards to monitor extraction efficiency<br />

<strong>and</strong> to quantify these analytes in the samples using an isotope dilution approach.<br />

Samples were extracted in toluene via Soxhlet <strong>and</strong> concentrated.<br />

Extracts were cleaned-up <strong>and</strong> PCDD/Fs were isolated through a series of<br />

chromatographic columns (U.S. EPA 1998). Analyses was performed using a<br />

high-resolution mass spectrometer coupled to a high-resolution gas chromatograph<br />

(HRGC-HRMS) equipped with a DB5 capillary chromatography<br />

column (60 m ´ 0.25 mm i.d. ´ 0.1 µm film thickness; J&W Scientific, Folsom,<br />

CA, USA). All analytical procedures were carried out according to protocols<br />

as described by U.S. EPA (1998).<br />

Statistics<br />

The statistical analyses were performed with the SAS statistical software<br />

package (SAS V8 <strong>and</strong> enterprise guide V1) <strong>and</strong> a significance level of p=0.05<br />

was used except where stated otherwise. Contaminant data was logtransformed<br />

(base e) prior to the analyses in order to meet the criteria of<br />

normality <strong>and</strong> homogeneity of the variance. The differences in the prevalence<br />

of periodontitis among periods, sex <strong>and</strong> agegroups were tested with X 2<br />

tests. The difference in organohalogen loads between the two groups with<br />

<strong>and</strong> without periodontitis was tested by a one-sample F-test.<br />

Results<br />

Periodontitis<br />

The age distribution over the entire period from 1892 to 2002 is viewed in<br />

Fig. 1 (not the large sampling from 1999 to 2002). In the 272 polar bear skulls<br />

that were examined for macroscopic pathological changes, we found cases of<br />

periodontitis, m<strong>and</strong>ibulare/frontale osseus proliferations, adonti (single<br />

tooth), deplacement of tooth, boneloss posterior to M1 <strong>and</strong> caries in incisivi,<br />

premolar <strong>and</strong> molar. In old polar bears (≥15 years of age) the severe cases of<br />

periodontitis were accompanied by loss of alveolar bone tissue <strong>and</strong> tooth<br />

wear. However, only periodontitis was found in frequencies that allowed for<br />

statistical analyses (Fig. 2).<br />

135

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