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Organohalogen concentrations and a gross and histologic ...

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SC<br />

II<br />

PC/LC<br />

Figure 2<br />

The histology of the enlarged clitoris from the 23-year-old female polar bear shot in Scoresby Sound, central East Greenl<strong>and</strong>, 1999.<br />

The ulcerated part of glans clitoridis is covered by serocellular crust (SC). The tissue is highly vascularized <strong>and</strong> there is intense<br />

inflammation (II) dominated by plasma cells (PC) <strong>and</strong> lymphocytes (LC), severe fibrosis (SF) <strong>and</strong> thrombosed capillaries (TC). Left:<br />

HE, 10x. Right: HE, 20x.<br />

<strong>and</strong> Scott 1993). The initial cause of the lesions can not be determined, but it<br />

is probable that some sort of trauma (e.g. mating, vestibulitis or vaginitis)<br />

have caused the first lesions. Subsequently, licking <strong>and</strong> biting of the lesions<br />

by this individual bear have caused further epithelial damage <strong>and</strong> persisting<br />

inflammatroy reaction with formation of granulated tissue. There was no<br />

signs of hyperplasia in the clitoral enlargement <strong>and</strong> therefore the female<br />

polar bear was not a pseudohermaphrodite (i.e. the enlargement was not<br />

due to endocrine disruption from <strong>and</strong>rogen or antiestrogen exposure).<br />

The uterine gl<strong>and</strong>s (crypts) were highly developed, indicating that this female<br />

had been in gestation earlier. Histological examination of the liver,<br />

kidneys, adrenals, spleen <strong>and</strong> lymph nodes showed only minor <strong>and</strong> insignificant<br />

changes (mainly mononuclear cell infiltrates) (Sonne et al., submitted-a,b).<br />

Concentrations of OCs <strong>and</strong> potential effects<br />

<strong>Organohalogen</strong>s<br />

Levels of ∑PCBs, ∑PBDEs, ∑DDTs, ∑HCHs <strong>and</strong> ∑CHLs in the adipose tissue<br />

of the 23-year-old female polar bear were compared with levels in 23<br />

adult female polar bears (age: 5-25 years) from East Greenl<strong>and</strong> (1999-2002)<br />

(Table 2). The <strong>concentrations</strong> of OHCs in this bear did not differ significantly<br />

from those in the reference group (all: p>0.05) except for ∑PCBs, which was<br />

slightly lower (p=0.04) (Table 2). ∑MeSO 2 -PCB <strong>and</strong> 3-MeSO 2 -4,4’-DDE <strong>concentrations</strong><br />

were not included in these comparisons due to covariance, i.e.,<br />

∑-MeSO 2 -PCB to ∑-PCBs <strong>and</strong> 3-MeSO 2 -4,4’-DDE to 4,4’-DDE ratios for the<br />

present Greenl<strong>and</strong> bears were relatively constant values of 0.08 ± 0.03 <strong>and</strong><br />

0.06 ± 0.05, respectively (S<strong>and</strong>ala et al., 2004). Additional information on OC<br />

<strong>concentrations</strong> <strong>and</strong> information on sex, season differences <strong>and</strong> time trends in<br />

the East Greenl<strong>and</strong> polar bear are available in Dietz et al., (2004) <strong>and</strong> S<strong>and</strong>ala<br />

et al., (2004).<br />

Recent studies on polar bears from Svalbard have correlated high levels of<br />

OCs to disruption of retinol (vitamin A), thyroid, sex steroids <strong>and</strong> cortisol<br />

levels in blood (Skaare et al., 2001; Haave et al., 2003, Oskam et al., 2003,<br />

2004) while other polar bear studies have indicated that high levels of OCs<br />

have a negative effect on IgG levels suggesting possible immunotoxic effects<br />

SF<br />

TC<br />

185

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