Zebrafish (Danio rerio) has been a prominent model vertebrate in a variety of biological disciplines. Substantial information gathered from developmental and genetic research, together with near-completion of the zebrafish genome project, has placed zebrafish in an attractive position for use as a toxicological model. Although still in its infancy, there is a clear potential for zebrafish to provide valuable new insights into chemical toxicity, drug discovery, and human disease using recent advances in forward and reverse genetic techniques coupled with large-scale, high-throughput screening. Here we present an overview of the rapidly increasing use of zebrafish in toxicology. Advantages of the zebrafish both in identifying endpoints of toxicity and in elucidating mechanisms of toxicity are highlighted.

Polycyclic aromatic hydrocarbons (PAHs), derived largely from fossil fuels and their combustion, are pervasive contaminants in rivers, lakes, and nearshore marine habitats. Studies after the Exxon Valdez oil spill demonstrated that fish embryos exposed to low levels of PAHs in weathered crude oil develop a syndrome of edema and craniofacial and body axis defects. Although mechanisms leading to these defects are poorly understood, it is widely held that PAH toxicity is linked to aryl hydrocarbon receptor (AhR) binding and cytochrome P450 1A (CYP1A) induction. Using zebrafish embryos, we show that the weathered crude oil syndrome is distinct from the well-characterized AhR-dependent effects of dioxin toxicity. Blockade of AhR pathway components with antisense morpholino oligonucleotides demonstrated that the key developmental defects induced by weathered crude oil exposure are mediated by low-molecular-weight tricyclic PAHs through AhR-independent disruption of cardiovascular function and morphogenesis. These findings have multiple implications for the assessment of PAH impacts on coastal habitats.

We report that the zebrafish mutation soulless, in which the development of locus coeruleus (LC) noradrenergic (NA) neurons failed to occur, disrupts the homeodomain protein Phox2a. Phox2a is not only necessary but also sufficient to induce Phox2b+ dopamine-beta-hydroxylase+ and tyrosine hydroxylase+ NA neurons in ectopic locations. Phox2a is first detected in LC progenitors in the dorsal anterior hindbrain, and its expression there is dependent on FGF8 from the mid/hindbrain boundary and on optimal concentrations of BMP signal from the epidermal ectoderm/future dorsal neural plate junction. These findings suggest that Phox2a coordinates the specification of LC in part through the induction of Phox2b and in response to cooperating signals that operate along the mediolateral and anteroposterior axes of the neural plate.

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on local circulation and apoptosis in the midbrain were investigated in zebrafish (Danio rerio) embryos during early development. Embryos were exposed to TCDD from 24 h post fertilization (hpf) until observation, in water maintained at 28.5 degrees C. TCDD decreased blood flow in the mesencephalic vein, the only vessel perfusing the dorsal midbrain of the embryo. At 50 hpf, blood flow was maximally reduced in this vessel and gradually returned to the control level at 60 hpf. In contrast, blood flows in the trunk and in other vessels of the head of the embryo did not significantly change until 72 hpf. Furthermore, TCDD exposure caused apoptosis in the midbrain at 60 hpf, and the TCDD dose response relationship for this effect was similar to that for reduced blood flow in the mesencephalic vein at 50 hpf. The effects of TCDD on apoptosis in the midbrain, but not on blood flow, were abolished by Z-VAD-FMK, a general caspase inhibitor. TCDD effects on both endpoints were mimicked by beta-naphthoflavone (BNF), an aryl hydrocarbon receptor (AHR) agonist, and almost abolished by concomitant exposure to TCDD and alpha-naphthoflavone (ANF), an AHR antagonist. Concomitant exposure to TCDD and either an inhibitor of cytochrome P450 (CYP) (SKF525A or miconazole) or an antioxidant (N-acetylcysteine or ascorbic acid) inhibited these effects of TCDD. The incidence of apoptosis in the midbrain was inversely related to blood flow in this brain region following these various treatments and graded TCDD exposure concentrations (r = -0.91). The same range of TCDD exposure concentrations that reduced blood flow and increased apoptosis in the midbrain greatly enhanced CYP1A mRNA expression and immunoreactivity at 50 hpf in endothelial cells of blood vessels including the mesencephalic vein and the heart, but not the brain parenchyma. Taken together, these results suggest that TCDD induces apoptosis in the midbrain of the zebrafish embryo secondary to local circulation failure, which could be related to AHR activation, induction of CYP1A, and oxidative stress.

It is widely believed that embryos and infants during development are highly sensitive to chemicals that cause serious damage to growth. However, knowledge on the mechanisms of developmental toxicity is scarce. One reason for this is limited convenient model system other than organ cultures using rodents to study the various aspects of developmental toxicology. Cultured cells are not always adequate for this purpose, since events in morphogenesis are processed through interactions with other tissues. We focused on zebrafish embryo (Danio rerio), one of the most important organisms in developmental biology. Saturation mutagenesis, applied to drosophila and nematode to define the functions of genes, has been carried out in zebrafish but almost no other vertebrate, and several thousand lines are available due to the rapid growth and transparent body of this embryo. Enhanced databases for the genome and ESTs are available at websites with abundant genetic and biological background. By targeted gene knock-down with morpholino-modified antisense oligonucleotieds (morpholinos), the translation of a specific protein can be transiently blocked for several days. Many reporter systems in vivo have been established mainly as GFP-transgenic fish for environmental chemicals. Although several excellent studies have been performed with zebrafish embryos on the effects of chemicals, the developmental toxicology of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) has been most extensively studied to date. We have found that TCDD induces apoptosis in dorsal midbrain with a concomitant decrease in local blood flow, using developing zebrafish. TCDD seems to produce oxidative stress through CYP1A induction in vascular endothelium, resulting in local circulation failure and apoptosis in the dorsal midbrain. In addition to applications in toxicology, an experimental system with zebrafish embryos could help to clarify the mechanism of congenital anomaly, which arises from genetic mutation.