The effects of diffusible creosote-derived compounds from weathered creosote-treated pilings on embryonic development in the Pacific herring were investigated. Parameters used to evaluate toxicity included embryonic development, cardiac function, embryo/larval activity (movement of developing embryos), hatching success, and larval morphology at hatch. For acute exposures, embryos were incubated in seawater containing either creosote-treated wood (creosote) or untreated wood (wood control), or seawater alone (control). All embryos adhering directly to creosote-treated wood and 40-50% of embryos not adhering to the creosote-treated wood failed to develop beyond the first few days of incubation. For surviving embryos, a 93% reduction in heart rate, and moderate to marked arrhythmia was observed. Surviving embryos also exhibited both an increase in frequency and an alteration in pattern of embryo/larval movement, with most embryos exhibiting tremors as compared with the vigorous movements of the control embryos. Cardiac function and embryo/larval movements of embryos exposed to untreated wood were not significantly different from controls. The hatching rate of embryos exposed to creosote was 90% lower than control embryos and 72.4% lower than embryos exposed to untreated wood, and the LC(50) for hatching success was 0.05 mg/l. Partial hatching (incomplete hatch) was observed in 15-20% of embryos exposed to creosote. All of the hatched larvae exposed as embryos to creosote exhibited morphological deformities, including scoliosis, pericardial edema and/or ascites. Similar effects were observed in embryos collected from creosoted pilings in San Francisco Bay, with a 72% decrease in hatching success compared with embryos collected from the Bay and severely deformed larvae. To investigate the combined effects of creosote and salinity on hatching success, larval morphology, and cardiac function, embryos were exposed to a sublethal concentration of creosote (0.003 mg/l) at three salinities; sub-optimal (8 parts per thousand (ppt)), optimal (16 ppt), and high salinity (28 ppt). The presence of creosote decreased hatching success at all three salinities, but the effect was greatest at 8 ppt (34% reduction) and the least in 28 ppt (14% reduction). The increased incidence of morphological abnormalities was also smallest at the high salinity (10% compared with 24 and 33% in 8 and 16 ppt). While exposure to creosote resulted in reduced heart rates at all three salinities, no additive effect of creosote and salinity was observed.