Toxicity and its detection in the dinoflagellate fish predatorsPfiesteria piscicida and Pfiesteria shumwayae depend on the strain and the use of reliable assays. Two assays, standardized fish bioassays (SFBs) with juvenile fish and fish microassays (FMAs) with larval fish, were compared for their utility to detect toxic Pfiesteria. The comparison included strains with confirmed toxicity, negative controls (noninducible Pfiesteria strains and a related nontoxic cryptoperidiniopsoid dinoflagellate), and P. shumwayae strain CCMP2089, which previously had been reported as nontoxic. SFBs, standardized by using toxic Pfiesteria (coupled with tests confirming Pfiesteria toxin) and conditions conducive to toxicity expression, reliably detected actively toxic Pfiesteria, but FMAs did not. Pfiesteria toxin was found in fish-and algae-fed clonal Pfiesteria cultures, including CCMP2089, but not in controls. In contrast, noninducible Pfiesteria and cryptoperidiniopsoids caused no juvenile fish mortality in SFBs even at high densities, and low larval fish mortality by physical attack in FMAs. Filtrate from toxic strains of Pfiesteria spp. in bacteria-free media was cytotoxic. Toxicity was enhanced by bacteria and other prey, especially live fish. Purified Pfiesteria toxin extract adversely affected mammalian cells as well as fish, and it caused fish death at environmentally relevant cell densities. These data show the importance of testing multiple strains when assessing the potential for toxicity at the genus or species level, using appropriate culturing techniques and assays.toxigenic dinoflagellates ͉ Pfiesteria piscicida ͉ Pfiesteria shumwayae

Methimazole is a compound administered to humans for the treatment of hyperthyroidism and is used experimentally as a model substrate for the flavin-containing monooxygenase (FMO) system. Previous results from this laboratory demonstrated that methimazole is an olfactory system toxicant, causing nearly complete destruction of the olfactory epithelium in the male Long-Evans rat following a single ip dose of 300 mg/kg.The present studies were undertaken to determine the dose-response relationship for methimazole-induced olfactory mucosal damage and to determine whether or not similar damage occurs as a result of oral administration, mimicking the relevant route of human exposure. We also investigated the mechanism of olfactory toxicity of methimazole by means of a structure-activity study and began the characterization of the form(s) of FMO present in the olfactory mucosa of the male Long-Evans rat. Dose-response analysis demonstrated that methimazole causes olfactory mucosal damage at doses of 25 mg/kg ip and greater. The results of gavage studies showed that a single oral dose of 50 mg/kg also caused olfactory mucosal damage. Two structurally related compounds, methylimidazole and methylpyrrole, were not olfactory toxicants, suggesting that a reactive intermediate generated in the course of metabolizing methimazole to an S-oxide is the olfactory toxic species. Microsomal incubation studies revealed the presence ofmethimazole S-oxidation activity in olfactory mucosal microsomes at levels comparable to those in liver. An anti-mouse liver FMO antibody reacted on Western blots with olfactory mucosal microsomes. These findings demonstrate a doseresponse for the olfactory toxicity of methimazole and suggest that characterization of human olfactory mucosal FMO activity may be necessary to assess the potential for human risk associated with therapeutic exposure to methimazole.

Ecosystem-level impacts of two hurricane seasons were compared several years after the storms in the largest lagoonal estuary in the U.S., the Albemarle-Pamlico Estuarine System. A segmented linear regression flow model was developed to compare mass-water transport and nutrient loadings to a major artery, the Neuse River Estuary (NRE), and to estimate mean annual versus storm-related volume delivery to the NRE and Pamlico Sound. Significantly less water volume was delivered by Hurricane Fran (1996), but massive fish kills occurred in association with severe dissolved oxygen deficits and high contaminant loadings (total nitrogen, total phosphorus, suspended solids, and fecal bacteria). The high water volume of the second hurricane season (Hurricanes Dennis, Floyd, and Irene in 1999) delivered generally comparable but more dilute contaminant loads, and no major fish kills were reported. There were no discernable long-term adverse impacts on water quality. Populations of undesirable organisms, such as toxic dinoflagellates, were displaced down-estuary to habitats less conducive for growth. The response of fisheries was species-dependent: there was no apparent impact of the hurricanes on commercial landings of bivalve molluscs or shrimp. In contrast, interacting effects of hurricane floodwaters in 1999 and intensive fishing pressure led to striking reductions in blue crabs. Overall, the data support the premise that, in shallow estuaries frequently disturbed by hurricanes, there can be relatively rapid recovery in water quality and biota, and benefit from the scouring activity of these storms.estuaries ͉ fisheries ͉ resilience ͉ volume delivery ͉ water quality