Laserfiche WebLink
• <br />• <br />common in the southeast. Northwards, quaking aspens become more frequent in the community. <br />The stature and spacing of trees is somewhat variable, reflecting differences in soils, topography, <br />and climate, factors that strongly affect local droughtiness and fire frequency. Small, gnarly, <br />open -grown trees are most common, although in moister spots, or in heavier soils, larger trees <br />are sometimes more common. Tree spacing ranges from sparsely and evenly distributed to <br />strongly clumped in moderately dense patches. Shrub cover is variable as well. The species <br />composition of the shrub layer depends somewhat upon soil characteristics. Oak grubs and <br />chokecherries are common on all soil types. On sandier soils, prairie willows (Salix humilis), <br />New Jersey tea (Ceanothus americanus), American hazelnuts (Corylus americana), sand cherries <br />(Prunus pumila), and juneberries (Amelanchier spp.) are usually present. Wolfberries <br />(Symphoricarpos occidentalis) are commoner on heavier soils. <br />Dry Oak Savanna occurs on the same kinds of landforms as Dry Prairie, except for bedrock <br />bluffs. Correspondingly, substrates range from excessively - drained to well - drained, sand to <br />loam soils. The presence of savanna rather than prairie indicates a lower fire frequency or <br />intensity (or both) than in prairie. Dry Oak Savanna requires less frequent fire than Mesic <br />Savanna for maintenance. However, in the complete absence of fire woodland will eventually <br />replace Dry Oak Savanna. Grazing and browsing animals may also have had a role in the <br />maintenance of Dry Oak Savanna. Because Dry Oak Savanna occurs on sites that are not as <br />suitable for cultivation as Mesic Savanna sites, and because succession in the absence of fire is <br />not as rapid, more examples remain of Dry Oak Savanna than of Mesic Oak Savanna. A <br />comprehensive plant species list for Foxborough's Oak Savanna restoration areas is provided in <br />Appendix B of this report. <br />Mesic Prairie <br />Mesic Prairies are upland grassland dominated by prairie species, with <10% tree cover and <br /><50% shrub cover ( <30% in far northwestern Minnesota), and NOT growing on steep slopes or <br />on sand- or gravel - dominated soil. Mesic Prairie is a type of Upland Prairie, which occurs <br />primarily in the prairie zone, with scattered occurrences in the deciduous forest - woodland zone. <br />Mesic Prairies are dominated by grasses. The tall grasses, big bluestem (Andropogon gerardii) <br />and Indiangrass (Sorghastrum nutans), are the major dominants on moist sites. Prairie dropseed <br />(Sporobolus heterolepis) is common on both dry and moist sites. Forbs typically are abundant <br />(but subdominant to the grasses) and may have high local diversity. Forb species composition <br />varies with site moisture, although some forb species occur on almost all sites, moist or dry. <br />Several low shrub or sub -shrub species are common on Upland Prairie; the most characteristic is <br />leadplant (Amorpha canescens). Taller brush and trees are absent or scattered, however brush or <br />woodland areas may be interspersed with prairie, usually in association with topographic and <br />aquatic features that provide protection from fire. <br />The most important cause of variation in species composition in prairie communities is variation <br />in soil moisture. The local soil moisture regime is determined by slope, aspect, proximity to the <br />water table, and soil texture. On a regional scale, variation in species composition is primarily <br />caused by climatic variation (i.e., the westward decline in precipitation and northward decline in <br />temperature in Minnesota). <br />Foxborough Conservation Development Restoration and Management Plan 19 <br />