Effect of an environmentally relevant metabolized organochlorine mixture on porcine cumulus–oocyte complexes☆
Introduction
Organochlorine compounds accumulate and bioamplify in the aquatic food web of circumpolar regions [1]. Several organochlorines such as polychlorinated biphenyls (PCBs), polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs), lindane, dichlorodiphenyl-trichloroethane (DDT) and hexachlorocyclohexane (HCH) are now formally banned or restricted under the United Nation's Stockholm Convention because of their physical properties and adverse effects on human health [1]. However, very high levels of these chemicals are still detected in wildlife species that are part of the traditional diet of aboriginal people in the Arctic region [1], [2], [3], [4].
In the body, organochlorine compounds are biotransformed into metabolites that may also be toxic and accumulate in the individual [2], [3], [4]. Exposure to organochlorines during pregnancy or lactation can adversely affect the reproductive system of the female offspring. In humans, exposure of mothers to DDT and its main metabolite p,p′-dichlorodiphenyldichloroethylene (p,p′-DDE) increased time to pregnancy and decreased fertility in the daughters [5]. In the rat, maternal PCB exposure decreased folliculogenesis in the female pups [6]. Exposing mice to lindane before and during early pregnancy lowered the number of blastomeres per morula and reduced the mitotic index of blastomeres [7].
Organochlorine compounds or their metabolites have been detected in semen, follicular fluid and genital tract fluid of humans [8], [9], [10], [11], [12], [13] and animals such as pigs, cattle and sheep [14], [15]. Levels of PCBs and organochlorines in follicular fluid are correlated to levels in plasma: follicular fluid concentrations were about one third of those in the serum [9], [12]. Developing oocytes are therefore directly exposed to organochlorines and their metabolites in the follicle.
Hence, exposing porcine oocytes during maturation to a mixture of organochlorines metabolized in vivo by sows and extracted from their plasma would be physiologically relevant. This would allow the oocytes to be exposed in vitro to the contaminants likely present in the ovaries in vivo. Therefore, not only would the oocytes be exposed to an environmentally relevant mixture of organochlorines as in our previous study [16], they would also be exposed to the mixture of organochlorine metabolites generated in vivo through biotransformation reactions. These metabolites could be ovotoxic by themselves or interact with the parent compounds to modulate their toxicity.
In an earlier study, we observed that exposing porcine oocytes to an environmentally relevant mixture of parent organochlorines decreased cumulus expansion, maturation and blastocyst formation [16]. The mixture also increased apoptosis in exposed cumulus cells and reduced the average number of cells in the blastocysts. Although the effects of organochlorines on oocyte maturation are becoming more established, no study has yet investigated the effects of direct exposure of a relevant organochlorine mixture containing both the parent compounds and their metabolites on oocyte competence during in vitro maturation.
This study was therefore designed to investigate the effect of a mixture of in vivo metabolized organochlorines, i.e. organochlorine metabolites extracted from sows to which the mixture was orally administered [17], [18] on porcine cumulus–oocyte complexes. We hypothesized that exposing oocytes to organochlorine metabolites would decrease maturation and subsequent development, as observed in our previous work with the parent organochlorine mixture [16].
Section snippets
Extraction of plasma samples containing organochlorines and their metabolites
In a previous study, pre-pubertal female pigs were fed corn oil (control) or an organochlorine mixture (100 μg PCBs/kg body weight/day) for 6–10 months [17]. Frozen pooled plasma (−20 °C) from control unexposed (385 ml) and exposed sows (710 ml) was processed in parallel. Equal volumes of ethanol and ammonium sulfate were added to the plasma and the resulting mixture was extracted three times with hexane. The organic phase was collected and the aqueous phase was acidified with a 50% sulfuric acid
Extraction of metabolites
Compounds present in the plasma extracts are presented in Table 1. The control (unexposed) sow extract contained only traces of organochlorines. Levels of most compounds were below the limit of detection of the analytical method. The product with the highest concentration in the control extract was pentachlorophenol at 10 μg/l. In the mixture composed of the metabolised organochlorine extract, p,p′-DDE was the most abundant constituent at 15.1 mg/l, accounting for 40.7% (relative concentration by
Discussion
This study is the first to evaluate the impact of organochlorine metabolites on oocyte competence in vitro. The COCs were exposed to a mixture of organochlorines that was metabolized in vivo, as they would be in the ovaries. Moreover, this study is original in that the oocytes were exposed to a range of organochlorine metabolite concentrations (up to 4.6 μg/l OH-PCBs and 15 μg/l p,p′-DDE) representative of those in the plasma of the Nunavik population (range = 0.12–11.6 ng/g OH-PCBs and 0.3–13.3 μg/l
Acknowledgements
The authors thank Pierre Dumas from the Laboratoire de toxicologie of the Institut national de santé publique du Québec for preparing the plasma extracts and performing the organochlorine analyses. We are also grateful to the Centre d’insémination porcine du Québec for donating semen and Salaisons Brochu slaughterhouse for the ovaries.
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This research was supported by the Northern Contaminants Program of Indian and Northern Affairs of Canada. C. Campagna was a recipient of an NSERC PhD scholarship.