Dh. Arnold et al., LANDTYPE-FOREST COMMUNITY RELATIONSHIPS - A CASE-STUDY ON THE MID-CUMBERLAND PLATEAU, Environmental monitoring and assessment, 39(1-3), 1996, pp. 339-352
Relationships between forest communities and landtypes (the most detai
led level of a hierarchical land classification system) were determine
d for the Prentice Cooper State Forest (PCSF), located on the southern
tip of Walden Ridge, west of Chattanooga, Tennessee. Four extensive l
andtypes within the Mullins Cove area of PCSF were sampled: 1) broad s
andstone ridges - south aspect (LT-3), 2) north sandstone slopes (LT-5
), 3) south sandstone slopes (LT-6), and 4) plateau escarpment and upp
er sandstone slopes and benches - south aspect (LT-17). Rectangular, 0
.04-hectare plots specified sub-plots for sampling overstory, midstory
, sapling/shrub, seedling/herb forest strata, and physical site charac
teristics. Plots (139) were allocated by landtype using a random start
with subsequent systematic location. Multivariate statistical techniq
ues were used to 1) examine the distinctness of forest communities occ
urring among landtypes (discriminant analysis), 2) describe the forest
communities occurring within landtypes (cluster analysis), and 3) det
ermine factors controlling the spatial distribution of forest communit
ies on the landscape (factor analysis). Different relative importance
values of species among communities along with different community com
binations among landtypes resulted in distinct forest vegetation among
landtypes. Chestnut oak (Quercus prinus L.), white oak (Quercus alba
L.), and shortleaf pine (Pinus echinata Miller) communities occurred o
n all four landtypes. Scarlet oak (Quercus coccinia Muenchh.) communit
ies occurred on LT-5, LT-6, and LT-17. Black oak (Quercus velutina Lam
.) communities occurred on LT-3 and LT-5. Yellow-poplar (Liriodendron
tulipifera L.), northern red oak (Querons rubra L.), and eastern hemlo
ck (Tsuga canadensis (L.) Carr.), communities occurred only on LT-17.
Landscape scale factors that varied along an elevation gradient were d
ominant in controlling spatial distribution of forest communities. Mic
rosite factors were secondary controllers. Specific ecological factors
could not be determined by factor analysis. Relatively distinct veget
ation occurs among sampled landtypes on the PCSF. This study provides
additional evidence that the land classification system divides the Mi
d-Cumberland Plateau landscape into distinct ecological units.