PCB disposition and different biological effects in rats following direct soil exposure vs. PCBs off-gassed from the soil

A comparison of PCB congener profiles and limited biological effects was made between direct exposure to PCB-contaminated soil and vapor phase PCBs from that soil to determine congener patterns useful for identifying exposure sources in humans and wildlife. Weanling female Sprague–Dawley rats were exposed to either control or PCB-contaminated soil (from a landfill in Southern Illinois) for 1 and 2 weeks. The exposures were via direct contact with the soil or via airborne exposure with the rats isolated from the soil by a wire screen. Total PCB of 25% contaminated soil used in the study was 13?500?ppm. No PCBs were detectable in control rats. In direct-exposed rats, total PCB residues in fat pad, ear skin, serum, liver, and inguinal lymph nodes after the 1-week exposure were 6256, 185, 3.2, 149, and 41?ppm, respectively, but decreased to 465, 72, 1.7, 106, and 32.4?ppm after the 2-week exposure. In airborne-exposed rats, total PCB residues were 7.8, 1.6, 0.03, 0.2, and 0.6 in the same manner and slightly increased in fat pad and ear skin to 11.6 and 2.14, respectively. Decreases in both the concentrations and percentages of “episodic” PCBs (those congeners rapidly metabolized) in the fat pad were apparent following the 2-week exposure compared to the 1-week exposure by both routes. Both EROD and BROD activities were significantly increased in the direct-exposed rats, whereas only BROD activity increased in airborne-exposed rats. Serum T ₄ levels were depleted in the direct-exposed rats regardless of time of exposure but were increased insignificantly after 1-week and significantly after 2 weeks in the airborne-exposed rats. No significant changes in serum insulin levels were apparent in any of the treated groups. The results suggested that exposure of animals to PCBs via different routes could result in different PCB profiles, which could cause different biological effects.