Increasing soil nutrients through litter manipulation, pollution, or fertilization can adversely affect ectomycorrhizal (EM) communities by inhibiting fungal growth. In this study, we used molecular genetic methods to determine the effects of litter addition on the EM community of a Pinus contorta stand in Yellowstone National Park that regenerated after a stand-replacing fire. Two controls were used; in unmodified control plots nothing was added to the soil, and in perlite plots perlite, a chemically neutral substance, was added to maintain soil moisture and temperature at levels similar to those under litter. We found that (i) species richness did not change significantly following perlite addition (2.6 Ű 0.3 species/core in control plots, compared with 2.3 Ű 0.3 species/core in perlite plots) but decreased significantly (P < 0.05) following litter addition (1.8 Ű 0.3 species/core); (ii) EM infection was not affected by the addition of perlite but increased significantly (P < 0.001) in response to litter addition, and the increase occurred only in the upper soil layer, directly adjacent to the added litter; and (iii) Suillus granulatus, Wilcoxina mikolae, and agaricoid DD were the dominant organisms in controls, but the levels of W. mikolae and agaricoid DD decreased significantly in response to both perlite and litter addition. The relative levels of S. granulatus and a fourth fungus, Cortinariaceae species 2, increased significantly (P < 0.01 and P < 0.05, respectively) following litter addition. Thus, litter addition resulted in some negative effects that may be attributable to moisture-temperature relationships rather than to the increased nutrients associated with litter. Some species respond positively to litter addition, indicating that there are differences in their physiologies. Hence, changes in the EM community induced by litter accumulation also may affect ecosystem function.Ectomycorrhizal (EM) fungi play a significant role in uptake and distribution of nutrients in temperate forest ecosystems, including the pine-dominated forests of the northern Rocky Mountains and Yellowstone National Park (9,13,14,40,42). Forest development often is fire driven and progresses from reestablishment of Pinus contorta (lodgepole pine) via serotinous cones through mixed P. contorta-Picea engelmannii (Engelmann spruce) or P. contorta-Abies lasiocarpa (subalpine fir) stands, depending on the soil conditions (41, 45). In the absence of fire, this progression to spruce-fir stands occurs in approximately 300 years. Litter accumulates and adds to the fire potential with the addition of the second tree species, and it continues to increase until fire reduces the fuel load.Fungal fruiting body (mushroom) assessments of EM fungal diversity indicate that patterns of EM diversity change during forest development. For example, after seedling establishment in young birch stands, EM fungal species diversity is relatively high. As stands age, the EM fungus species composition changes, the EM fungal diversity decreases, and a diffe...