title: Development and validation of a chronic Pb bioavailability model for the freshwater rotifer Brachionus calyciflorus.
abstract: The univariate effects of Ca, pH, and dissolved organic carbon (DOC) on chronic (48-h) Pb toxicity to the freshwater rotifer Brachionus calyciflorus were investigated. High pH (8.2) and higher concentrations of DOC were protective against filtered Pb toxicity, whereas Ca was not. However, expressed as the free Pb2+ion, Pb2+toxicity increased with increasing DOC concentration, indicating that Pb-fulvic acid (FA) complexes may be bioavailable and may contribute to toxicity. Two different bioavailability models were developed. The pH effect was modeled as a single-site competition effect by H+(log KHBL= 7.14). In the first model, only this H+effect was considered; in a second model, a log-linear fulvic acid bioavailability effect (SFA= 0.602) was also incorporated. Both models predicted chronic Pb toxicity for most waters used for model development within a 2-fold error. To validate the predictive capacities of the models, chronic Pb toxicity to B. calyciflorus was tested in 5 natural waters and a reference water. Both models consistently underestimated Pb toxicity in the natural waters, as a result of a shift in rotifer sensitivity to Pb between the development and the validation test series. However, optimizing the intrinsic sensitivity in the models specific for the validation test series resulted in reasonable predictions of Pb toxicity in the natural waters. The second, more complex model predicted chronic Pb toxicity most accurately. The protective effects of water chemistry on Pb toxicity to Brachionus are comparable to those observed for Ceriodaphnia. However, the developed Brachionus models were not able to accurately predict chronic Pb toxicity to the rotifer Philodina rapida. It remains unclear why the influence of water chemistry on chronic Pb toxicity appears to be different between 2 rotifer species. Environ Toxicol Chem 2016;35:2977-2986. © 2016 SETAC.
authors.affiliation: Faculty of Bioscience Engineering, GhenToxLab, Ghent University (UGent), Ghent, Belgium.
authors.forename: Charlotte
authors.initials: C
authors.lastname: Nys
authors.affiliation: Faculty of Bioscience Engineering, GhenToxLab, Ghent University (UGent), Ghent, Belgium.
authors.forename: Colin R
authors.initials: CR
authors.lastname: Janssen
authors.affiliation: Faculty of Bioscience Engineering, GhenToxLab, Ghent University (UGent), Ghent, Belgium.
authors.forename: Karel A C
authors.initials: KA
authors.lastname: De Schamphelaere
mesh_terms: D000818:Animals; D001578:Benzopyrans / Q000737:chemistry; D001682:Biological Availability; D002118:Calcium / Q000737:chemistry; D056831:Coordination Complexes / Q000737:chemistry / Q000378:metabolism / Q000633:toxicity; D005618:Fresh Water / Q000737:chemistry; D006863:Hydrogen-Ion Concentration; D007854:Lead / Q000032:analysis / Q000378:metabolism / Q000633:toxicity*; D008962:Models, Theoretical; D012403:Rotifera / Q000187:drug effects / Q000378:metabolism; D013054:Spectrophotometry, Atomic; D014874:Water Pollutants, Chemical / Q000032:analysis / Q000378:metabolism* / Q000633:toxicity
chemical_list: D001578:Benzopyrans; D056831:Coordination Complexes; D014874:Water Pollutants, Chemical; D007854:Lead; D002118:Calcium; C005023:fulvic acid
keywords: Biotic ligand model; Lead; Metal bioavailability; Risk assessment; Water quality criteria