Historically, the vegetation of Otome Highland, Yamanashi Prefecture, central Japan, was maintained by mowing and dominated by tall forbs. However, forbs have been replaced by Miscanthus sinensis, a tall grass, since around 2005, coinciding with an increase in the sika deer population (Cervus nippon). Eleven representative plant species were cut 10 cm above the ground. Among nine forb species, six species died after cutting, and the surviving three species regrew to a shorter height than that of the control plants. Conversely, M. sinensis and Lespedeza bicolor, a shrub, not only survived but showed no decrease in height over the long term by cutting. M. sinensis was cut in June, September or November, and both June and September. These treatments were continued for 5 years. November cutting did not affect grass height. June cutting reduced grass height, but this height was maintained over 5 years. September cutting and June/September cutting steadily reduced the height over 5 years. Grazing by deer affected the survival and height of forbs, but M. sinensis was slightly or not affected, which explained the replacement of forbs by M. sinensis in Otome Highland. A deer proof fence of 15 ×15 m was set in the M. sinensis community. After 4 years, M. sinensis was reduced, and tall forbs had greatly increased or recovered inside the fence. This resulted in an increase in diversity among the plant community inside the fence (H′ = 2.64), which was three times greater than that outside (H’ = 0.85). Changes in dominant plants in the upper layer of the plant community from tall forbs to M. sinensis affected low-growing ground plants. Thelypteris palustris, a short fern, was increased among clumps of M. sinensis. Potentilla freyniana, a prostrate forb, also increased with M. sinensis outside the fence but was decreased with an elongated petiole height inside the fence. This study demonstrated that deer grazing affects plant communities by three different mechanisms:1) deer preference (unpalatable plants are untouched), 2) plant response (e.g., ability of plants to recover after defoliation or physical removal of plant parts), and 3) indirect effects of canopy-forming plants on ground plants. From these results, we concluded that the replacement of tall forbs by the M. sinensis plant community since 2005 was a result of sika deer grazing.
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