Mandates to develop non-mammalian models for chemical immunotoxicity evaluation: are fish a viable alternate to rodents?

Hazardous properties and toxicological update of mercury: From fish food to human health safety perspective

The mercury (Hg) poisoning of Minamata Bay of Japan widely activated a global attention to Hg toxicity and its potential consequences to the aquatic ecosystem and human health. This has resulted to an increased need for a dynamic assembly, contextualization, and quantification of both the current state-of-the-art and approaches for understanding the cause-and-effect relationships of Hg exposure. Thus, the objective of this present review is to provide both hazardous toxic properties and toxicological update of Hg, focusing on how it ultimately affects the aquatic biota to potentially produce human health effects. Primarily, we discussed processes that relate to Hg exposure, including immunological aspects and risk assessment, vulnerability, toxicokinetics, and toxicodynamics, using edible fish, swordfish (Xiphias gladius), as a model. In addition, we summarized available information about Hg concentration limits set by different governmental agencies, as recognized by national and international standardization authorities.

Vulnerable windows for developmental ethanol toxicity in the Japanese medaka fish (Oryzias latipes)

Ethanol (EtOH) is a well-known developmental toxicant that produces a range of abnormal phenotypes in mammalian systems including craniofacial abnormalities, cognitive deficits and growth retardation. While the toxic potential of developmental EtOH exposure is well characterized clinically, the effect of timing on the extent of toxicity remains unknown. Fish models such as the Japanese medaka, Oryzias latipes, provide a convenient system for investigating the effects of developmental EtOH exposure in vivo. In this study, medaka embryo toxicity tests were used to assess temporal variations in developmental EtOH toxicity. Fertilized eggs were collected and incubated during early, middle or late egg development (e.g., 0-3, 3-6 or 6-9 days post-fertilization) with various sub-lethal concentrations of EtOH [0.1% (17.2 mM), 0.5% (86.0 mM) or 1% (172 mM)]. Uptake of EtOH by the embryo was 60-68% of the solution concentration across all windows. Time to hatch, head width, total body length and whole embryo caspase activity were used to assess toxicity. Hatching delays were noted only at the highest concentration of EtOH. Head width was affected at all ethanol levels, regardless of the window of exposure. EtOH-induced decreases in body length, however, appeared to be most pronounced when exposure occurred either during the first or last window. The effect on caspase-3/7 activity also depended on the window of exposure, with increases in caspase noted in embryos treated on days 1 or 2 (first window) and decreases seen in embryos treated on day 6 (second window) or day 8 (third window). In general, these data suggest that critical periods for heightened sensitivity to developmental EtOH exposure may vary according to the specific endpoint used to assess toxicity.

Evaluation of fish models of soluble epoxide hydrolase inhibition

Substituted ureas and carbamates are mechanistic inhibitors of the soluble epoxide hydrolase (sEH). We screened a set of chemicals containing these functionalities in larval fathead minnow (Pimphales promelas) and embryo/larval golden medaka (Oryzias latipes) models to evaluate the utility of these systems for investigating sEH inhibition in vivo. Both fathead minnow and medaka sEHs were functionally similar to the tested mammalian orthologs (murine and human) with respect to substrate hydrolysis and inhibitor susceptibility. Low lethality was observed in either larval or embryonic fish exposed to diuron [N-(3,4-dichlorophenyl), N'-dimethyl urea], desmethyl diuron [N-(3,4-dichlorophenyl), N'-methyl urea], or siduron [N-(1-methylcyclohexyl), N'-phenyl urea]. Dose-dependent inhibition of sEH was a sublethal effect of substituted urea exposure with the potency of siduron < desmethyl diuron = diuron, differing from the observed in vitro sEH inhibition potency of siduron > desmethyl diuron > diuron. Further, siduron exposure synergized the toxicity of trans-stilbene oxide in fathead minnows. Medaka embryos exposed to diuron, desmethyl diuron, or siduron displayed dose-dependent delays in hatch, and elevated concentrations of diuron and desmethyl diuron produced developmental toxicity. The dose-dependent toxicity and in vivo sEH inhibition correlated, suggesting a potential, albeit undefined, relationship between these factors. Additionally, the observed inversion of in vitro to in vivo potency suggests that these fish models may provide tools for investigating the in vivo stability of in vitro inhibitors while screening for untoward effects.

Analysis of apoptosis of lymphoid cells in fish exposed to immunotoxic compounds

BACKGROUND

Chemical induction of apoptosis in cells is believed to contribute to toxicity. Techniques for measuring apoptosis have increased in both sensitivity and number and in many cases can be readily extended to nontraditional research species. A comparison of established assays for measuring apoptosis of lymphoid cells has thus far not been performed in the fish and thus would be efficacious in assessing immunotoxicity.

METHODS

The present study evaluated chemical-induced immune cell apoptosis in fish (tilapia, Oreochromis niloticus) exposed to two known immunotoxic chemicals, azathioprine and T-2 toxin. Cytocentrifugation and light microscopy of leukocyte-enriched cell samples from the pronephros (i.e., the fish primary hematopoietic compartment) demonstrated chemical-related increases in apoptotic bodies. This observation was examined further with the ApoAlert Annexin V Apoptosis kit and two DNA-binding dyes employed for detecting apoptosis, 7-aminoactinomycin D (7-AAD) and propidium iodide (PI).

RESULTS

The apoptotic probes confirmed the microscopic observations of increased apoptosis in the chemical-exposed fish. The ApoAlerttrade mark annexin V and 7-AAD assays, which discriminate early and late apoptosis/necrosis, compared well in identifying apoptotic populations. PI staining in Vindelov's solution was unable to detect early apoptosis.

CONCLUSIONS

The present data suggest that apoptotic immune cells may be a useful marker for certain immunotoxicant exposures in fish. These findings agree with those of previous reports that fish may respond immunologically in a manner similar to mammals after immunotoxicant challenge.