Mercury (Hg), Selenium (Se), and Arsenic (As) found in coal combustion wastes (CCW) and radionuclides released from anthropogenic activities present potential environmental and human health concerns. Despite the widespread harvest and consumption of wildlife by recreational hunters, game species are not subject to the same safety testing as commercially marketed livestock; thus, there are few data available regarding contaminant concentrations in many commonly harvested wildlife. We sampled feral pigs (Sus scrofa; invasive wild pigs), gray squirrels (Sciurus carolinensis), and waterfowl from relatively uncontaminated habitats and areas of contamination to quantify levels of trace elements and radiocesium (137Cs) in muscle and liver tissues for assessment of potential human health risks from the consumption of game. Species collected at a CCW ash basin consistently had levels of selected trace elements, particularly Se, above concentrations considered toxic to waterfowl, suggesting CCW may be an important pathway for wildlife, and subsequently human exposure to this element. Similarly, we observed elevated concentrations of 137Cs in wildlife collected in or near aquatic ecosystems with histories of operational releases of radionuclides. The majority of tissue samples analyzed were below elemental levels known to adversely affect wildlife health and 137Cs levels were below European Economic Community limits for human consumption established following the 1986 Chernobyl accident. Waterfowl, however, had levels of several elements of interest (Se and Hg) that could be of health concern to the birds, especially individuals collected from areas with known contamination, or human consumers of the birds. Given the high levels of trace element burdens we observed in waterfowl collected from ash basins, and the common occurrence of similar surface impoundments throughout much of the globe, wide‐scale sampling for contaminants in waterfowl within or across migratory flyways appear to be greatly needed to better understand routes of contaminant movement and potential areas (or species) with elevated contamination risk to waterfowl and hunters. © 2017 The Wildlife Society.

Low-level releases of radiocesium into former nuclear reactor cooling-reservoirs on the U.S. Department of Energy's Savannah River Site (SRS) in South Carolina, USA, dating primarily to the late 1950s and early 1960s, have allowed examination of long-term contaminant attenuation in biota occupying these habitats. Periodic collections of migratory game birds since the 1970s have documented Cs (radiocesium) activity concentrations in birds of SRS reservoirs, including mainly Par Pond and Pond B. In this study, during 2014 and 2015 we released wild-caught American coots (Fulica americana) and ring-necked ducks (Aythya collaris) onto Pond B. We made lethal collections of these same birds with residence times ranging from 32 to 173 days to examine radiocesium uptake and estimate the rate of natural attenuation. The two species achieved asymptotic whole-body activity concentrations of radiocesium at different times, with ring-necked ducks requiring almost three times longer than the 30-35 days needed by coots. We estimated ecological half-life (T) for Pond B coots over a 28-yr period as 16.8 yr (95% CI = 12.9-24.2 yr). Pond B coot T was nearly four times longer than T for coots at nearby Par Pond where radiocesium bioavailability had been constrained for decades by pumping of potassium-enriched river water into that reservoir. T could not be estimated from long-term data for radiocesium in Pond B diving ducks, including ring-necked ducks, likely because of high variability in residence times of ducks on Pond B. Our results highlight the importance: (1) for risk managers to understand site-specific bio-geochemistry of radiocesium for successful implementation of countermeasures at contaminated sites and (2) of residence time as a critical determinant of observed radiocesium activity concentrations in highly mobile wildlife inhabiting contaminated habitats.