Abstract:A 96-h, static, nonconstant exposure design was used to assess pharrnacokinetic parameters and to identify the rate-limiting process in polychlorinated biphenyl (PCB) uptake by golden shiners (Notemigonus crysoleucus). Fish were exposed individually to I4C-labeled PCBs corresponding to Aroclor 1254 (A1254). After various intervals (2-96 h), fish and water were analyzed for total radioactivity. Uptake of PCBs and decline of the external water concentration were both rapid. A clearance constant-based one-compart… Show more
“…Nyholm et al applied the same nonlinear regression model to tests with Scenedesmus subspicatus and Selenastrum capricornutum, measuring the growth inibition toxicity due to K 2 Cr 2 O 7 . Sigmoid curves have often been applied to interprete results of experiments measuring uptake of organic compounds by organisms [29][30][31][32][33][34].…”
Abstract-Chemical analyses and bioassays were used in conjunction to assess the quality of sediments of the Venice lagoon. Organic micropollutants (polycyclic aromatic hydrocarbons [PAHs] polychlorinated biphenyls [PCBs], and chlorinated pesticides) were extracted from sediment samples and analyzed by gas chromatography after fractionation into classes of compounds. The Vibrio fischeri test was used to assess the acute toxicity of sediment extracts. The test was applied to organic extracts before cleanup and to extracts purified from sulfur and fractionated into single classes of compounds. Extracts before purification were much more toxic than single fractions. In particular, sulfur was toxic to V. fischeri. For PAHs and PCBs the 50% effective concentration (EC50) and EC20 values were determined using natural and spiked extracts (EC50 ϭ 0.5 g/ml and 1.4 g/ml, respectively; EC20 ϭ 0.13 g/ml and 0.17 g/ml). Sensitivity limits of the method for these compounds were also estimated as was an EC50 value of elemental sulfur dissolved in ethanol (0.022 g/ml). A mathematical model was used to fit the concentration-response data to a sigmoid curve.
“…Nyholm et al applied the same nonlinear regression model to tests with Scenedesmus subspicatus and Selenastrum capricornutum, measuring the growth inibition toxicity due to K 2 Cr 2 O 7 . Sigmoid curves have often been applied to interprete results of experiments measuring uptake of organic compounds by organisms [29][30][31][32][33][34].…”
Abstract-Chemical analyses and bioassays were used in conjunction to assess the quality of sediments of the Venice lagoon. Organic micropollutants (polycyclic aromatic hydrocarbons [PAHs] polychlorinated biphenyls [PCBs], and chlorinated pesticides) were extracted from sediment samples and analyzed by gas chromatography after fractionation into classes of compounds. The Vibrio fischeri test was used to assess the acute toxicity of sediment extracts. The test was applied to organic extracts before cleanup and to extracts purified from sulfur and fractionated into single classes of compounds. Extracts before purification were much more toxic than single fractions. In particular, sulfur was toxic to V. fischeri. For PAHs and PCBs the 50% effective concentration (EC50) and EC20 values were determined using natural and spiked extracts (EC50 ϭ 0.5 g/ml and 1.4 g/ml, respectively; EC20 ϭ 0.13 g/ml and 0.17 g/ml). Sensitivity limits of the method for these compounds were also estimated as was an EC50 value of elemental sulfur dissolved in ethanol (0.022 g/ml). A mathematical model was used to fit the concentration-response data to a sigmoid curve.
“…Nyholm et al applied the same nonlinear regression model to tests with Scenedesmus subspicatus and Selenastrum capricornutum , measuring the growth inibition toxicity due to K 2 Cr 2 O 7 . Sigmoid curves have often been applied to interprete results of experiments measuring uptake of organic compounds by organisms [29–34].…”
Chemical analyses and bioassays were used in conjunction to assess the quality of sediments of the Venice lagoon. Organic micropollutants (polycyclic aromatic hydrocarbons [PAHs] polychlorinated biphenyls [PCBs], and chlorinated pesticides) were extracted from sediment samples and analyzed by gas chromatography after fractionation into classes of compounds. The Vibrio fischeri test was used to assess the acute toxicity of sediment extracts. The test was applied to organic extracts before cleanup and to extracts purified from sulfur and fractionated into single classes of compounds. Extracts before purification were much more toxic than single fractions. In particular, sulfur was toxic to V. fischeri. For PAHs and PCBs the 50% effective concentration (EC50) and EC20 values were determined using natural and spiked extracts (EC50 = 0.5 μg/ml and 1.4 μg/ml, respectively; EC20 = 0.13 μg/ml and 0.17 μg/ml). Sensitivity limits of the method for these compounds were also estimated as was an EC50 value of elemental sulfur dissolved in ethanol (0.022 μg/ml). A mathematical model was used to fit the concentration–response data to a sigmoid curve.
“…In natural systems, however, the aqueous concentration may significantly and continuously change over time through dynamic processes of volatilization, sedimentation, and biochemical degradation, such that the steady-state equilibrium conditions are rarely established (Newman and Jogue, 1996). Even in dynamic exposure experiments, it is a constraint to maintain constant aqueous concentrations of chemicals in these systems (Karara and McFarland, 1992). Bioaccumulation itself can also cause significant changes of aqueous concentrations not accounted for in constant concentration models.…”
Much attention has been paid to the bioaccumulation of toxicants in aquatic organisms during the last several years. In order to accurately predict and assess toxicant fate in natural ecosystems, most efforts have employed mathematical models to determine the relationship between aqueous concentrations and organism accumulation (Barron et al 1990;Landrum et al. 1992;Newman, 1995). In most cases, bioaccumulation models are based on the assumption that the concentration in water remains constant over the exposure time period. Thus, many exposure experiments are designed to achieve constant aqueous concentration of chemicals using dynamic flow-through systems (Bruggeman, 1981).Constant exposure regimes greatly simplify the estimation of bioconcentration factor (BCF) as well as the model kinetics. In natural systems, however, the aqueous concentration may significantly and continuously change over time through dynamic processes of volatilization, sedimentation, and biochemical degradation, such that the steady-state equilibrium conditions are rarely established (Newman and Jogue, 1996). Even in dynamic exposure experiments, it is a constraint to maintain constant aqueous concentrations of chemicals in these systems (Karara and McFarland, 1992). Bioaccumulation itself can also cause significant changes of aqueous concentrations not accounted for in constant concentration models. In order to describe the bioaccumulation processes in the laboratory as well as in natural systems more accurately, these models should incorporate the changes of concentrations in both the water phase, as well as in aquatic organisms. This paper presents a bioaccumulation model where the concentrations of toxicants continuously change over time both in organisms and in water while incorporating volatilization, biochemical degradation, or sediment interaction terms. This model was developed based on a mass balance numerical approach and validated against data obtained from the bioaccumulation of trans-and cischlordane into goldfish (Carassius auratus).
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