National attention has been focused on Yellowstone's northern elk winter range since the early 1930s. Scientists and managers then believed that grazing and drought in the early part of the century had reduced the range's carrying capacity, and that twice as many elk were on the range in 1932 as existed in 1914. From 1935 to 1968, elk, pronghorn, and bison numbers were artificially controlled by shooting or trapping and removal by park rangers. Then in the 1960s, based on new studies that suggested ungulate populations could possibly be self-regulating, elk reductions were discontinued in the park. The belief that elk grazing was damaging to northern range vegetation and that grazing accelerates erosion, although not supported by research data and analysis, has continued to the present. Studies of the northern elk winter range began in the 1960s and revealed no clear evidence of range overuse (Houston 1982). More recent studies conclude that sagebrush grasslands of Yellowstone's northern winter range are not overgrazed (Singer and Bishop 1990). In fact, plant production was enhanced by ungulate grazing in all but drought years. Protein content of grasses, yearly growth of big sagebrush, and seedling establishment of sagebrush were all enhanced by ungulate grazing. Neither reduction in root biomass nor an increase in dead bunchgrass clumps was observed. However, many questions remain concerning the condition of riparian zones and associated shrubby vegetation; the park hopes to conduct additional studies on aspen and willows and their relationship to ungulates on the northern range.