Selenium bioaccumulation by the water boatman Trichocorixa reticulata (Guerin-Meneville).

The input of selenium from subsurface agricultural drainage into surface water systems can result in the accumulation of toxic concentrations of selenium in aquatic food chains. Elevated selenium concentrations in aquatic systems is a significant environmental problem in many areas of the United States. A laboratory investigation was conducted to determine the dominant route of selenium bioaccumulation by the corixid Trichocorixa reticulata, an important food chain organism. The roles of waterborne and foodborne exposure in selenium bioaccumulation were examined using 48-h bioassays. Waterborne selenium concentrations ranged from 0 to 1,000 microgram Se/L as selenate. A mixture of two species of blue-green algae cultured in media with selenium concentrations ranging from 0 to 1,000 microgram Se/L as selenate was used as a corixid diet in the foodborne treatments. Corixids exposed to waterborne selenate did not accumulate selenium above control concentrations. Corixids fed algae exposed to >/=100 microgram Se/L as selenate had significantly higher selenium concentrations than control organisms. These data suggest that corixids may be effectively isolated from the water and selenium accumulation is solely through dietary exposure.

Role-played interpersonal interaction: ecological validity and cardiovascular reactivity.

Conflictual role-play scenarios have been used to model brief interpersonal interaction and to elicit cardiovascular reactivity in the laboratory. Here we discuss data suggesting that role-played interactions constitute an ecologically valid laboratory task that may improve laboratory-to-field generalization of cardiovascular response. Specifically, our research indicates that young adults perceive the stress associated with role-play scenarios as similar to that encountered in everyday life. Furthermore, these stress appraisals moderate cardiovascular response to role-play in men. We also find that a social stressor (i.e. speech task) is perceived as significantly more similar to a real-life stressor as compared to other standard laboratory tasks. We propose that particular constellations of cognitive, affective, and behavioral responses to laboratory-based social stressors, such as role-played interaction, may elicit different patterns of hemodynamic response. Further understanding of interrelations among cognitive, affective, behavioral, and physiological response patterns may assist in the study of cardiovascular reactivity as a potential mechanism linking personality factors and the development of cardiovascular disease.

Ecotoxicology of selenium in freshwater systems.

The toxicology, environmental impacts and risk assessment of Se in freshwater systems are a high priority for research and regulatory agencies. However, understanding Se in freshwater systems is a challenging endeavor. The accurate risk assessment and determination of a water-quality criterion for any freshwater ecosystem are difficult for many reasons. First, the understanding of the structure and energy dynamics in ecosystems is limited. Second, knowledge of Se cycling and transformations in aquatic ecosystems is rudimentary. Third, the role of various environmental factors affecting its bioaccumulation, biotransformation, and toxicology in aquatic ecosystems is largely unknown. Fourth, the extrapolation and use of existing data in commonly used formulas for risk assessment and calculations of water quality criteria is difficult because of the demonstrated species differences in the bioaccumulation, metabolism, and tolerance of Se. There are many aspects of Se ecotoxicology that need to be addressed to develop more accurate environmental risk assessments and determine appropriate water-quality criteria to protect aquatic ecosystems. Studies evaluating the biochemical speciation of Se in aquatic ecosystems, and determination of the role of microbial communities in its cycling, bioaccumulation, transformation, transfer, and toxicity in aquatic systems, appear to be priorities for future research. These would include a broad exploration of Se effects on ecosystems, e.g., exposure regime, direct and indirect biologic effects, and ecosystem level effects. There are, however, ecological uncertainties that tend to confound such endeavors, e.g., insufficient data, extrapolation issues, and environmental stochasticity (Harwell and Harwell 1989). There are several concepts concerning the ecotoxicology of Se that can be stated. Elevated concentrations have degraded many freshwater ecosystems throughout the United States, and additional systems are expected to be affected as anthropogenic activities increasingly mobilize Se into aquatic systems. Se is a very toxic essential trace element. Toxic threshold concentrations in water, dietary items, and tissues are only 2-5 times normal background concentrations. Toxicity in freshwater ecosystems is the result of bioaccumulation, biotransformation, and cycling of Se in aquatic food chains. Thus, environmental risk assessment and development of effective water-quality criteria to protect freshwater ecosystems become formidable tasks.