Abstract:Organochlorine and mercury levels in wild mink (Mustela vison) and otter (Lutra canadensis) from eight areas of New York State were measured in adipose and liver tissues. Polychlorinated biphenyl (PCB) compounds, quantified as Aroclor 1254/1260 and p,p'‐DDE, were detected in all animals. Significantly greater concentrations of organochlorines in both species were associated with habitat known to be contaminated with PCB (Hudson Valley and within 5 mi of Lake Ontario). Wet‐weight PCB concentrations in adipose t… Show more
“…(Stejskal et al 1989). Mercury concentrations in liver tissue of Illinois mink are lower than those reported from wild mink in New York (Foley et al 1988) but similar to those reported in liver, kidney and muscle tissue from wild mink collected in less polluted regions of Ontario (Wren et al 1986). Mercury concentrations in liver tissue of Illinois mink are lower than those reported from wild mink in New York (Foley et al 1988) but similar to those reported in liver, kidney and muscle tissue from wild mink collected in less polluted regions of Ontario (Wren et al 1986).…”
: Mink and otters are valuable wildlife resources and management efforts in North America and Europe have been directed towards re-establishing extirpated populations or expanding existing populations. The similarity of otter and mink habits and trophic status may allow inferences about the suitability of the habitat that is occupied by one species (mink) for the other species that is absent (otter). Remnant otter populations in Illinois have not expanded even though suitable habitat appears to be available and is occupied by mink. Low contaminant concentrations in tissues of mink trapped in a habitat where otters are not found and metal and organochlorine concentrations in tissues of otters incidentally collected by the Illinois Department of Natural Resources, suggest that environmental contaminants should not hinder natural expansion of otters in Illinois.
“…(Stejskal et al 1989). Mercury concentrations in liver tissue of Illinois mink are lower than those reported from wild mink in New York (Foley et al 1988) but similar to those reported in liver, kidney and muscle tissue from wild mink collected in less polluted regions of Ontario (Wren et al 1986). Mercury concentrations in liver tissue of Illinois mink are lower than those reported from wild mink in New York (Foley et al 1988) but similar to those reported in liver, kidney and muscle tissue from wild mink collected in less polluted regions of Ontario (Wren et al 1986).…”
: Mink and otters are valuable wildlife resources and management efforts in North America and Europe have been directed towards re-establishing extirpated populations or expanding existing populations. The similarity of otter and mink habits and trophic status may allow inferences about the suitability of the habitat that is occupied by one species (mink) for the other species that is absent (otter). Remnant otter populations in Illinois have not expanded even though suitable habitat appears to be available and is occupied by mink. Low contaminant concentrations in tissues of mink trapped in a habitat where otters are not found and metal and organochlorine concentrations in tissues of otters incidentally collected by the Illinois Department of Natural Resources, suggest that environmental contaminants should not hinder natural expansion of otters in Illinois.
“…For example, fatty acid signatures and carbon and nitrogen stable isotopes in herring gulls sampled between 1978 and 2005 have indicated a decline in fi sh consumption, and this corresponded well with decreased levels of contaminants in their eggs (Hebert et al 2008 ) . Others have reported that varying levels of mercury in local prey fi sh relate well with mercury levels in mink and river otter tissues (Cumbie 1975 ;Kucera 1983 ;Wren et al 1986 ;Foley et al 1988 ) .…”
Section: Environmental Exposures To Methylmercurymentioning
The purpose of this chapter is to provide an overview of how piscivorous (fi sh-eating) wildlife can be used to complement existing public health strategies to assess the neurotoxic risks of methylmercury. A brief introduction concerning the use of wildlife as model sentinel organisms in the fi eld of environmental neurotoxicology is provided. Next, selected scientifi c examples are detailed that illustrate how data from piscivorous wildlife may provide pertinent, real-world information on the bioavailability of methylmercury and environmental exposures. Information concerning methylmercury's subclinical (e.g., perturbations in brain neurochemistry and neuroendocrine hormones) and clinical (structural and functional defi cits) neurological effects across organisms is also discussed.
“…As top level piscivorous predators, osprey (Pandion haliaetus), otter (Lutra sp.) and mink are generally considered to be representative barometers of aquatic/semi-aquatic ecosystem health [10,[64][65][66][67][68][69][70][71]. Interestingly, the use of mink and otter as sentinels/bio-indicators or related sample types, as both pertain to factors such as contaminant body burden, have been called into question [72,73].…”
Section: Case Study 1: Chronic Exposure Of River Otters To Nsaids In mentioning
Pharmaceutical residues in the environment have the potential to harm wildlife. A population's fragility or an animal's secretive nature may preclude capture and the use of invasive/destructive sampling techniques that are typically used in a risk assessment. Conventionally favoured matrices gathered opportunistically from carcasses have a finite lifespan, thereby limiting the detection window. This multidisciplinary paper aims to promote the use of non-invasive approaches and optimize use of even the most degraded carcasses. We highlight a selection of promising alternative, unconventional and underutilized sample types that could be applied in environmental monitoring efforts and wildlife forensic investigations. With a focus on non-steroidal anti-inflammatory drugs (NSAIDs), now under increasing scrutiny in the freshwater and terrestrial environment, we first illustrate current sampling practices and gaps in knowledge by summarizing exposure of: 1) aquatic organisms to urban effluent discharged into waterways, and, 2) scavenging species to veterinary residues in livestock and other carrion. We then consider the merits and limitations of a range of alternative environmentally robust sample options that offer a broader detection interval for NSAIDs, with emphasis on hair, wool and feathers. The viability of eyes/ocular material, bone matter, fecal matter, injection sites, ingesta/pellets and scavenging/coprophagous insects are also discussed.
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