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Cadmium (Cd) is a well-described environmental pollutant known to have adverse effects in fish, including behavioral deficits. We have previously reported the development of an in vivo system that utilizes hsp70 gene activation as a measure of acute 3 h cadmium toxicity in whole living transgenic zebrafish larvae carrying a stably integrated hsp70-enhanced green fluorescent protein (eGFP) reporter gene. Here, we report that activation of this transgene in olfactory epithelium of zebrafish larvae during 96 h sublethal Cd exposure is predictive of cadmium-induced cell death, altered histological and surface organization of the epithelium, and changes in olfactory dependent behavior. The transgene is first activated in the olfactory epithelium at concentrations below those giving rise to significant defects, but exhibits a more robust response following exposure to Cd at concentrations that begin to cause significant cell death, morphological alterations, and behavioral deficits. Further, the data show that Cd-induced olfactory deficits reported previously in juvenile and adult fish can also occur during larval stages of fish development, and that such behavioral deficits are closely associated with cell death and structural alterations in the olfactory epithelium.

Iron acquisition from various ferric chelates and colloids was studied using iron‐limited cells of Anabaena flos‐aquae (Lyng.) Brèb UTEX 1444, a cyanobacterial strain that produces high levels of siderophores under iron limitation. Various chelators of greatly varying affinity for Fe3+ (HEDTA, EDDHA, desferrioxamine mesylate, HBED, 8‐hydroxyquinoline) were assayed for the degree of iron acquisition by iron‐limited cyanobacterial cells. Iron uptake rates (measured by graphite furnace atomic absorption spectrometry) varied approximately inversely with calculated [Fe3+] (calculated as pFe) and decreased with increasing chelator‐to‐iron ratio. No iron uptake was observed when Fe3+ was chelated with HBED, the strongest of the tested chelators. Iron‐limited Anabaena cells were able to take up iron from 8‐hydroxyquinoline (oxine or 8HQ), a compound sometimes used to quantify aquatic iron bioavailability. Iron bound to purified humic acid was poorly available but did support some growth at high humic acid concentrations. These results suggest that for cyanobacteria, even tightly bound iron is biologically available, including to a limited extent iron bound to humic acids. However, iron bound to some extremely strong chelators (e.g. HBED) is likely to be biologically unavailable.

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