PATTERNS AND DRIVERS OF RIPARIAN FOREST VEGETATION CHANGESĀ OVER LAST HALF CENTURY IN SOUTHERN WISCONSIN
In the canopy, we observed significant shifts in the relative abundances and sizes of notable lowland forest tree species, indicating impacts of disease and hydrologic regime changes. Ulmus spp. (elms) have declined in abundance and in size due to Dutch elm disease. These declines have contributed to significant increases in rapidly growing, flood-tolerant species such as Fraxinus spp. (ash) along unregulated rivers. Along dam-regulated rivers flood-intolerant and shade-tolerant species such as Carya cordiformis (bitternut hickory) have increased in abundance. Accompanying these increases in later-successional flood intolerant species are significant declines in early colonizing, flood-tolerant species and key species such as Quercus bicolor (swamp white oak). Acer saccharinum (silver maple) was the dominant species across many sites in the 1950s and has become even more dominant along rivers experiencing increased growing season flow (m3/s).
Sites adjacent to large rivers and surrounded by more contiguous forest showed the greatest increases in native understory diversity since the 1950s. In more fragmented and urbanizing landscapes where floods are rare, woody and exotic plants have increased in the understory, accompanied by losses of native species diversity. However, species diversity remains high at sites prone to frequent flooding even in fragmented landscapes. As natural flooding regimes appear to best maintain native species diversity in fragmented landscapes, managers should seek to recreate these whenever feasible.