Interior Plateau
By Mark A. Drummond 1
Click to see available downloads for this ecoregion

Figure 1. Interior Plateau
and surrounding ecoregions. The 40 randomly selected 100-km² sample blocks are
shown along with land use/land cover from the 1992 National Land Cover Dataset.
Ecoregion
Description
The
Interior Plateau ecoregion is a series of grassland plateaus and forested
uplands that are generally lower in elevation than the Appalachian Mountains to
the east but higher than the plains to the south. The ecoregion has a total
area of approximately 127,810 km2 (49,348 mi2) and covers
large areas of western Kentucky and central Tennessee, as well as parts of Indiana, Alabama, and Ohio (fig. 1). The Ohio River, which runs along the northern border
of Kentucky, drains most of the northern part of the ecoregion.
The
relatively flat and fertile lowlands, which include the Bluegrass area of
central Kentucky and the Nashville Basin in central Tennessee, attracted early
settlement and farming. Today, those areas are highly populated, including the
cities of Louisville, Kentucky, and Nashville, Tennessee. The Pennyroyal
Plateau in south-central Kentucky and northern Tennessee is a dense
agricultural area that also contains a distinctive “flatwood” ecosystem. The
area is characterized by oak forests and wet conditions that are caused by an
underlying hard, dense fragipan soil (Chester and others, 1995).
Rapid
subsurface drainage occurs in sinkhole areas such as south-central Kentucky where extensive cave systems wind through the karst limestone landscape. Water
quality of the associated aquifers and streams is a special concern in
watersheds where agriculture and coal mining are prevalent.
Ecoregion-wide,
climate conditions are humid temperate and average about 1,200 mm (47.2 in) of
annual precipitation. Oak-hickory stands are the most common forest type,
although mixed stands of red cedar and hardwoods grow on many of the rockier
sites and limestone glades (fig 2). Blue-stem prairie is the most common
grassland. Historically, fire was an important natural process for maintaining
open-canopied, savannah-like conditions on the plateaus (Chester and others,
1995; Hudson, 2002).
Population
has increased steadily, by approximately 40 percent between 1970 and 2000, from
4.4 million to 6.2 million people. Automobile manufacturing has expanded into
the area, and tourism and service industries are also important in several locations.
Major agricultural products include soybeans, corn, tobacco, and dairy (fig 3).
The Bluegrass area has unique land uses, including a tradition of race horse
breeding and training farms and the production of high-value burley tobacco.
Contemporary Land Cover
Change from 1973 to 2000
The
Interior Plateau had a relatively low rate of overall land cover change when
compared to other Eastern ecoregions (fig. 4). Between 1973 and 2000, 4.3
percent of the ecoregion underwent change, and 95.7 percent of the total area
was stable. An estimated 3.6 percent of the ecoregion changed once. The
percentage of area that underwent multiple changes was relatively low. An
estimated 0.7 percent of the area changed twice, and 0.1 percent changed three
times (table 1).
The
highest total change occurred between 1980 and 1986 (1.7 percent), with an
annual rate of 0.28 percent (table 2 and fig. 5). The lowest rate of change
occurred during the period between 1973 and 1980, when total change was less
than 1 percent (0.8 percent) and the annual rate was 0.12 percent.
Agriculture,
forest, and developed lands account for more than 96 percent of the ecoregion.
Agriculture is the major land cover and comprised 50.9 percent of the ecoregion
in 1973, declining to 50 percent in 2000 (table 3). Forest was the next highest
cover type, with a high of 39 percent in 1973 and a low of 37.7 percent in
2000. Developed land had a steady gain, from 6.9 percent in 1973 to 8.6
percent in 2000 (fig 6). Other small gains of approximately 0.2 percent each
occurred in the mechanically disturbed and the grassland/shrubland categories.
Developed
land expanded the most, with a 1.7 percent increase between 1973 and 2000
(table 3). Net losses occurred in forest and agriculture, with net declines of
1.3 percent and 0.8 percent, respectively. Although development generally accelerated
over the 27-year study period (fig. 7), the highest rate of expansion was
between 1980 and 1986 (0.6 percent), which is also the period with the highest
overall rate of ecoregion change (1.7 percent). The majority of the conversion
to development, nearly 60 percent, occurred from agriculture. Conversely, the
majority of agricultural loss was to development, except in the 1973 to 1980
period when the conversion of agriculture to grassland was highest.
Between
1973 and 2000, the most common conversion (1,373 km2 or 530 mi2)
was from forest cover to agriculture (table 4). However, this conversion did
not result in a net increase in agriculture because at the same time
agricultural lands were being converted to developed land and to
grassland/shrubland at an overall higher rate. Conversion from agriculture to
developed land was the second most common change (1,250 km2 or 483
mi2). The various gains and losses of agriculture are masked by a
low net rate of change (–0.8 percent). Cyclic changes involving mechanical
disturbance of forest and subsequent reforestation were less common, although
they increased through time (fig 8).
References
Chester,
E.W., Noel, S.M., Baskin, J.M., Baskin, C.C., and McReynolds, M.L., 1995, A phytosociological
analysis of an old-growth upland wet woods on the Pennyroyal Plain,
southcentral Kentucky, USA: Natural Areas Journal, v. 15, p. 297–307.
Hudson, J.C., 2002, Across this land—A
regional geography of the United States and Canada: Baltimore, The Johns
Hopkins University Press, 474 p.
Table 1. Estimated overall
spatial land cover change between 1973 and 2000
|
|
Overall
|
Number of changes
|
|
|
spatial change
|
1
|
2
|
3
|
4
|
|
Percent of
ecoregion
|
4.3
|
3.6
|
0.7
|
0.1
|
0.0
|
Table 2. Total and annual rates
of land cover change for each time interval
|
|
Period
|
|
|
1973–1980
|
1980–1986
|
1986–1992
|
1992–2000
|
|
Total
change (% of ecoregion)
|
0.8%
|
1.7%
|
1.4%
|
1.6%
|
|
Margin of
error (85% confidence level)
|
+/–0.2%
|
+/–0.5%
|
+/–0.4%
|
+/–0.4%
|
|
Average
annual rate of change (%/year)
|
0.1%
|
0.3%
|
0.2%
|
0.2%
|
Table 3. Land cover area,
including net change
|
|
1973
|
1980
|
1986
|
1992
|
2000
|
Net change 1973–2000
|
|
Land-use/land-cover
class
|
km²
|
%
|
km²
|
%
|
km²
|
%
|
km²
|
%
|
km²
|
%
|
km²
|
%
|
|
Water
|
1,976
|
1.5
|
1,986
|
1.6
|
1,993
|
1.6
|
2,009
|
1.6
|
2,026
|
1.6
|
50
|
0.0
|
|
Developed
|
8,859
|
6.9
|
9,087
|
7.1
|
9,829
|
7.7
|
10,291
|
8.1
|
11,011
|
8.6
|
2,152
|
1.7
|
|
Mechanically
disturbed
|
37
|
0.0
|
18
|
0.0
|
127
|
0.1
|
150
|
0.1
|
322
|
0.3
|
285
|
0.2
|
|
Mining
|
111
|
0.1
|
230
|
0.2
|
138
|
0.1
|
176
|
0.1
|
161
|
0.1
|
51
|
0.0
|
|
Naturally
barren
|
1
|
0.0
|
1
|
0.0
|
1
|
0.0
|
1
|
0.0
|
1
|
0.0
|
0
|
0.0
|
|
Forest
|
49,864
|
39.0
|
49,532
|
38.8
|
48,981
|
38.3
|
48,710
|
38.1
|
48,149
|
37.7
|
–1,715
|
–1.3
|
|
Grassland/Shrubland
|
1,021
|
0.8
|
1,161
|
0.9
|
1,278
|
1.0
|
1,265
|
1.0
|
1,263
|
1.0
|
243
|
0.2
|
|
Agriculture
|
65,005
|
50.9
|
64,831
|
50.7
|
64,524
|
50.5
|
64,269
|
50.3
|
63,938
|
50.0
|
–1,067
|
–0.8
|
|
Wetland
|
935
|
0.7
|
943
|
0.7
|
938
|
0.7
|
939
|
0.7
|
938
|
0.7
|
3
|
0.0
|
|
Non-mechanically
disturbed
|
0
|
0
|
21
|
0
|
0
|
0.0
|
0
|
0.0
|
0
|
0.0
|
0
|
0.0
|
Table 4. Leading land cover
conversions for the four time periods of the study
|
|
|
|
Area changed
|
% of all
|
|
Period
|
From
class
|
To
class
|
(km2)
|
changes
|
|
1973–1980
|
Forest
|
Agriculture
|
218
|
20
|
|
|
Agriculture
|
Grassland/Shrubland
|
210
|
19
|
|
|
Grassland/Shrubland
|
Forest
|
124
|
11
|
|
|
Forest
|
Developed
|
105
|
10
|
|
|
Agriculture
|
Developed
|
103
|
10
|
|
|
Other
classes
|
Other
classes
|
320
|
30
|
|
|
|
|
1,080
|
100
|
|
|
|
|
|
|
|
1980–1986
|
Agriculture
|
Developed
|
464
|
22
|
|
|
Forest
|
Agriculture
|
460
|
22
|
|
|
Forest
|
Developed
|
235
|
11
|
|
|
Agriculture
|
Grassland/Shrubland
|
207
|
10
|
|
|
Grassland/Shrubland
|
Forest
|
195
|
9
|
|
|
Other
classes
|
Other
classes
|
574
|
27
|
|
|
|
|
2,135
|
100
|
|
|
|
|
|
|
|
1986–1992
|
Forest
|
Agriculture
|
365
|
21
|
|
|
Agriculture
|
Developed
|
281
|
16
|
|
|
Grassland/Shrubland
|
Forest
|
218
|
13
|
|
|
Agriculture
|
Grassland/Shrubland
|
193
|
11
|
|
|
Forest
|
Developed
|
125
|
7
|
|
|
Other
classes
|
Other
classes
|
544
|
32
|
|
|
|
|
1,726
|
100
|
|
|
|
|
|
|
|
1992–2000
|
Agriculture
|
Developed
|
403
|
20
|
|
|
Forest
|
Agriculture
|
330
|
17
|
|
|
Forest
|
Mechanically
disturbed
|
288
|
15
|
|
|
Forest
|
Developed
|
240
|
12
|
|
|
Agriculture
|
Forest
|
165
|
8
|
|
|
Other
classes
|
Other
classes
|
556
|
28
|
|
|
|
|
1,982
|
100
|
|
Overall:
|
|
|
|
|
|
1973–2000
|
Forest
|
Agriculture
|
1,373
|
20
|
|
|
Agriculture
|
Developed
|
1,250
|
18
|
|
|
Forest
|
Developed
|
704
|
10
|
|
|
Agriculture
|
Grassland/Shrubland
|
694
|
10
|
|
|
Grassland/Shrubland
|
Forest
|
663
|
10
|
|
|
Other
classes
|
Other
classes
|
2,239
|
32
|
|
|
|
|
6,923
|
100
|

Figure 1. Interior Plateau
and surrounding ecoregions. The 40 randomly selected 100-km² sample blocks are
shown along with land use/land cover from the 1992 National Land Cover Dataset.

Figure 2. A roadside vista
of pastureland, forest and farms in the central part of the ecoregion,
south-central Kentucky.

Figure 3. A tobacco field
in central Tennessee.

Figure 4. Overall spatial
change from 1973 to 2000 for all Eastern U.S. ecoregions. The entire bar shows
the overall spatial change, while the gradients indicate the percent of
ecoregion area that changed during one or multiple periods.

Figure 5. Estimates of land
cover change per time interval normalized to annual rates of change.

Figure 6. Interstate 24 and
suburban development outside of Nashville, Tennessee.

Figure 7. Land cover
changes are shown for the four time intervals of the study.

Figure 8. Forest clearance
near the eastern edge of the ecoregion.