The ringtail (Bassariscus astutus) attains the northern limit of its range in southwestern Oregon (Hall 1981:964, map 500). In Oregont as in most regionsJ B. astutus is not abundant; estimates of density elsewhere usually are < 5 per km2 (Poglayen-Neuwall and Toweill 1988). It is classified as a sensitive species-undetermined status't by the Oregon Department of Fish and Wildlife on infrequent sightings or reports and is afforded protection against taking in Oregon by state administrative rule (Marshall 1992:RING 1). Other than information contained in general works on mammals (e.g./ Bailey 1936), we know of no published report concerning any aspect of the biology of B. astutus in Oregon. Knowledge of the species elsewhere is fragmentary, especially in comparison with that of most other North American carnivoresX In 1992, a project was initiated by one of us (TPF) to investigate several aspects of the ecology of B. nstutus in the Myrtle Creek drainage, a tributary of the South Umpqua River, northeast of Myrtle Creek, Douglas Co., Oregon (T 28 S, R 3-4 W). Habitats occupied by B. astutus were in Douglas-fir (Pseudotsuga menziesii) forest at elevations of 450-550 m. Most of the area was occupied by regenerating 5-30-yr-old clear-cuttings with older Douglas-fir forest and riparian hardwoods interspersed. Bassariscus astutus usually denned in 15-30-m Douglas-fir snags, but dens occasionally were located in brush piles, downed logs, and stumps. Fifty-six fecal droppings were collected at entrances to dens or at the base of trees containing dens occupied by five B. astutus to which beacon radio transmitters were attached. Dens and individuals were located and identified by radio signals at unique frequencies; nevertheless, all fecal droppings may not have been deposited by the radio-tagged individual occupying a specific den. Herein, we report on the diet of B. astutus in Oregon based on our examination and identification of food remains in those fecal droppings. Fecal droppings were placed in plastic bags, labeled, and frozen. Examination of the droppings followed procedures outlined by Korschgen (1980). Briefly, individual fecal droppings were softened by soaking in water then teased apart and the material distributed fairly evenly over 21 x 32-cm white-enameled trays. Materials that could not be identified in the trays or when picked out and examined under a 7-30 x binocular microscope were dried on paper towels and placed in labeled envelopes for subsequent comparison with museum specimens or identification by specialists of specific taxonomic groups. Results are reported by frequency of occurrence and percent frequency of occurrence by month (Table 1); samples were available for 9 of the 12 months. The diet of B. astutus in Oregon (Table 1) is similar to that reported for the species elsewhere in that it is omnivorous (Grinnell et al. 1937; Taylor 1954; Trapp 1978; Toweill and Teer 1977). Similar proportions of fecal samples contained materials of plant and animal origin (Table 1). Plant material occurred in 93% of the samplesr similar to the 90.6% reported by Toweill and Teer (1977) for the Edwards Plateau in Texas. Trappe (1978) reported 46% of samples from Utah contained fruits, 17% miscellaneous vegetable matter, and 4% graminoids, considerably less frequent than we found among Oregon samples (even if the Utah frequencies were additive). Direct comparison of our findings with those of Taylor (1954), Wood (1954), and Davis (1960) conducted in Texas was not possible because they did not present data by frequency of occurrence. In our study, leaves, scales, and bracts of several conifers; wood; moss; and lichens were consumed throughout the year, whereas berries and seeds were consumed only during summer (August-September; Table 1). Conifer leaves were incorporated into the feces, not merely stuck to themr indicating that the leaves actually were ingested, but on passing through the digestive tract of B. astutus, the leaves exhibited little change. Most other items in the feces were well masticated and/ except for hard items (bone, teeth, chitin, seeds, hair, and cellulose), heavily digested. Ninety-one percent of the samples also contained animal material. Mammal remains were tound in 66% of the samples, considerably more frequent than the 13.7% reported by Toweill and Teer (1977) in Texas, and slightly more than the 55% reported in Utah (Trapp, 1978). Murid rodents were the largest component of the mammalian food items (Table 1), likely reflecting the nocturnal foraging habits of B. astutus (Poglayen-Neuwall and Toweill 1988). Among mammals represented, the red tree vole (Phenacomys longicaudus) occurred most frequently. The house cat (Felis catus), represented