Seasonal woodland pools are at tremendous risk due to habitat degradation and loss. Current conservation measures for this habitat type focus on protection from loss, however, non-point source pollution (such as mercury (Hg)) and disease are emerging concerns. This interdisciplinary research characterized the chemical environment of pool water, litter, and sediment to 2 cm depth in four short-hydroperiod (inundated three to nine weeks) seasonal woodland pools in Acadia National Park (ANP), Maine, USA, during April-June 2008 and upon October refill to determine (1) the rate of Hg bioaccumulation by developing wood frogs (Lithobates sylvaticus), (2) influences of surrounding landscape, seasonal hydrology, and pool water chemistry on Hg burdens in wood frog embryos and tadpoles, and (3) potential for transport into the terrestrial food chain through metamorph emigration from pools. We chose pools in regions of ANP with different landscape features and contrasting burn histories. There were no strong temporal patterns in upland and wetland litter total Hg (THg), however, THg in sediment was greatest at pool dry down in June. Upon October refill, THg in pool water in the unburned region equaled or exceeded June concentrations, whereas, THg in pool water in the burned region was at concentrations measured at April ice-out. Total Hg concentrations measured in wood frog embryos collected within 1-2 weeks of egg deposition (mid-April) were near or below detection limits (<0.2 ng; 0-0.49 ppb, wet weight(ww)). Concentrations increased to 17.1-54.2 ppb ww in tadpoles at final collection in early to mid-June when pools were nearly dry. At that time methyl Hg (MeHg) comprised 7.2-42.0% of THg in wood frog tadpoles, comparable to the proportion of THg that was MeHg in 2-3 year old green frog (L. clamitans) and bullfrog (L. catesbeiana) tadpoles collected in permanent water bodies in nearby watersheds (Bank et al. 2007), indicating rapid Hg uptake in wood frogs. Water collected from pools surrounded by softwoods had lower pH and greater THg and dissolved organic carbon than water from pools in hardwood settings. Total Hg concentrations in tadpoles, however, did not clearly reflect pool conditions or landscape setting. The relatively rapid bioaccumulation of THg in the developing larvae indicates that wood frog metamorphs could be potential vectors of Hg from wetlands to terrestrial food webs.