North Central Appalachians
By Kristi L. Sayler 1
Click to see available downloads for this ecoregion

Figure 1. North Central
Appalachians and surrounding ecoregions. The 10 randomly selected 400-km²
sample blocks are shown along with land use/land cover from the 1992 National
Land Cover Dataset.
Ecoregion
Description
The
North Central Appalachians ecoregion (fig. 1) is a forested, sedimentary upland
that is punctuated by high hills and low mountains (Woods and others, 1996).
The ecoregion covers approximately 30,500 km2 (11,700 mi2)
and is divided into two separate portions. The unglaciated western portion
lies along the headwaters of the Allegheny and Susquehanna Rivers in north central Pennsylvania with a sliver in southern New York. This forested
landscape supports the major economic activities of forestry and recreation (fig.
2 and 3). This part of the ecoregion is also at the northern fringe of the
Appalachian coal belt and includes substantial portions of Pennsylvania’s oil
and gas production (Woods and others, 1996). The eastern portion comprises the
Pocono Mountains of Pennsylvania and portions of the Catskill Mountains of New
York and New Jersey, which range from low mountains to rolling hills with a
dissected plateau at the eastern edge of the Allegheny Front (Ackroyd-Kelly,
1987). This area has historically provided an accessible, rural recreation
oasis for generations of residents of nearby New York and Philadelphia. The
climate of the North Central Appalachians ecoregion can be characterized as
continental, with cool summers and cold winters. The average annual
precipitation ranges from 825 to 1,250 mm (33 to 50 in).
Contemporary Land Cover
Change (1973 to 2000)
The overall spatial change from 1973 to 2000 for the North Central
Appalachians was 6.2 percent (table 1), a fairly low amount of change compared
to other Eastern U.S. ecoregions (fig. 4). Of the 6.2 percent estimated area
of change, nearly half of the land changed multiple times. The change per time
period ranged between 1.5 percent and 2.9 percent with margins of error ranging
from 0.7 to 1.4 percent (table 2). The average annual rates of change (fig. 5)
showed that the 1980 to 1986 period had the greatest amount of change with an
average rate of 0.4 percent per year (table 2). This number would have been
substantially lower had there not been an outbreak of around 42 tornadoes on
May 31, 1985 (Monfredo, 1999), which deforested a significant portion of the
ecoregion. The tornado damage and its subsequent return to pre-storm land cover
made up about 8.1 percent of the total change between 1980 and 2000 in the
ecoregion.
Forest made up 87.4 percent of
the land cover in 1973, and it decreased only 0.8 percent during the study period
to 86.7 percent in 2000 (table 3). This decrease is mostly attributed to
forest clear-cutting in the ecoregion and forest loss caused by tornado
activity in 1985 (fig. 6). These clear-cuts primarily represent the harvesting
of hardwood trees for lumber and other wood products and are shown as
conversions from forest to the mechanically disturbed land cover class (fig. 7).
The area is known for its exceptionally high quality of black cherry, with
other hardwoods commonly harvested, including yellow poplar, white ash, red
maple, and sugar maple (Napton and others, 2003).
Both mining and developed lands had very small increases in all time
periods. Surface coal mining, quarries, gravel pits, and natural gas field
developments all contributed to the 0.3 percent increase in mining. Developed
lands increased slightly (0.4 percent), primarily in the eastern portion of the
ecoregion where the proximity to the Poconos and Catskills regions makes it
possible for individuals to have second homes and still live and work near New York City (fig. 8).
The leading land cover conversions were all related to the vast forests
of the North Central Appalachians ecoregion. Forest to mechanically disturbed
and mechanically disturbed to forest were the top two land cover conversions
during all time periods (table 4). These two conversions were related to the
forest harvest and regrowth cycles of the timber industry of the ecoregion.
The other main land cover change agent was the tornado activity, shown as a
forest to non-mechanically disturbed conversion in 1980 to 1986 and the
subsequent conversion of non-mechanically disturbed to forest as the affected
forest areas regenerated (table 4). Overall, these conversions accounted for
82.4 percent of the area changed in the ecoregion.
References
Ackroyd-Kelly, I.H., 1987, The near country—the
historical geography of Pocono resorts: The Pennsylvania Geographer, v. 25,
no. 1, p. 18-23.
Monfredo, W., 1999, Significant tornado activity in
southwestern Pennsylvania: The Pennsylvania Geographer, v. 37, no. 2, p.
43-63.
Napton, D., Sohl, T.L., Auch, R.F., and Loveland, T.R., 2003, Land use and land cover change in the North Central Appalachians
ecoregion: The Pennsylvania Geographer, v. 41, no.2, p. 46-66.
Woods, A.J., Omernik, J.M., Brown, D.D., and
Kiilsgaard, C.W., 1996, Level III and IV ecoregions of Pennsylvania and the
Blue Ridge Mountains, the Ridge and Valley, and Central Appalachians of
Virginia, West Virginia, and Maryland: EPA/600/R-96/077, U.S. Environmental Protection
Agency, National Health and Environmental Effects Research Laboratory,
Corvallis, Oreg., 50 p.
Table 1. Amount of overall
spatial change detected in ecoregion and proportion of ecoregion that
experienced change during one or multiple time periods
|
|
Overall
|
Number of changes
|
|
|
spatial change
|
1
|
2
|
3
|
4
|
|
Percent of
ecoregion
|
6.2
|
3.5
|
2.6
|
0.1
|
0.0
|
Table 2. Raw estimates of
percent change in ecoregion computed for each of four time periods and
associated margin of error at 85-percent confidence level
|
|
Period
|
|
|
1973-1980
|
1980-1986
|
1986-1992
|
1992-2000
|
|
Total
change (% of ecoregion)
|
1.5%
|
2.3%
|
2.2%
|
2.9%
|
|
Margin of
error (85% confidence level)
|
+/-0.8%
|
+/-1.4%
|
+/-0.7%
|
+/-0.7%
|
|
Average
annual rate of change (%/year)
|
0.2%
|
0.4%
|
0.4%
|
0.4%
|
Table 3. Proportion of
ecoregion covered by each land cover class during each of five mapped dates
|
|
1973
|
1980
|
1986
|
1992
|
2000
|
Net change 1973-2000
|
|
Land-use/land-cover
class
|
km²
|
%
|
km²
|
%
|
km²
|
%
|
km²
|
%
|
km²
|
%
|
km²
|
%
|
|
Water
|
451
|
1.5
|
447
|
1.5
|
451
|
1.5
|
455
|
1.5
|
428
|
1.4
|
-22
|
-0.1
|
|
Developed
|
400
|
1.3
|
409
|
1.3
|
426
|
1.4
|
452
|
1.5
|
481
|
1.6
|
81
|
0.3
|
|
Mechanically
disturbed
|
298
|
1.0
|
358
|
1.2
|
251
|
0.8
|
420
|
1.4
|
448
|
1.5
|
151
|
0.5
|
|
Mining
|
118
|
0.4
|
117
|
0.4
|
143
|
0.5
|
195
|
0.6
|
247
|
0.8
|
129
|
0.4
|
|
Barren
|
1
|
0.0
|
1
|
0.0
|
1
|
0.0
|
1
|
0.0
|
1
|
0.0
|
0
|
0.0
|
|
Forest
|
26684
|
87.4
|
26621
|
87.2
|
26638
|
87.3
|
26490
|
86.8
|
26417
|
86.6
|
-267
|
-0.9
|
|
Grassland/Shrubland
|
1
|
0.0
|
1
|
0.0
|
1
|
0.0
|
1
|
0.0
|
1
|
0.0
|
0
|
0.0
|
|
Agriculture
|
2256
|
7.4
|
2252
|
7.4
|
2186
|
7.2
|
2171
|
7.1
|
2175
|
7.1
|
-82
|
-0.3
|
|
Wetland
|
313
|
1.0
|
315
|
1.0
|
312
|
1.0
|
309
|
1.0
|
321
|
1.1
|
8
|
0.0
|
|
Non-mechanically
disturbed
|
0
|
0.0
|
0
|
0.0
|
112
|
0.4
|
28
|
0.1
|
2
|
0.0
|
2
|
0.0
|
Table 4. Leading land cover
conversions during each of four time periods
|
|
|
|
Area changed
|
% of all
|
|
Period
|
From
class
|
To
class
|
(km2)
|
changes
|
|
1973-1980
|
Forest
|
Mechanically
disturbed
|
210
|
45
|
|
|
Mechanically
disturbed
|
Forest
|
162
|
35
|
|
|
Forest
|
Mining
|
22
|
5
|
|
|
Agriculture
|
Forest
|
16
|
3
|
|
|
Mining
|
Mechanically
disturbed
|
14
|
3
|
|
|
Other
classes
|
Other
classes
|
39
|
8
|
|
|
|
|
463
|
100
|
|
|
|
|
|
|
|
1980-1986
|
Mechanically
disturbed
|
Forest
|
268
|
39
|
|
|
Forest
|
Mechanically
disturbed
|
162
|
23
|
|
|
Forest
|
Non-mechanically
disturbed
|
108
|
16
|
|
|
Agriculture
|
Forest
|
63
|
9
|
|
|
Forest
|
Mining
|
35
|
5
|
|
|
Other
classes
|
Other
classes
|
58
|
8
|
|
|
|
|
694
|
100
|
|
|
|
|
|
|
|
1986-1992
|
Forest
|
Mechanically
disturbed
|
305
|
45
|
|
|
Mechanically
disturbed
|
Forest
|
136
|
20
|
|
|
Non-mechanically
disturbed
|
Forest
|
83
|
12
|
|
|
Forest
|
Mining
|
61
|
9
|
|
|
Forest
|
Developed
|
27
|
4
|
|
|
Other
classes
|
Other
classes
|
64
|
9
|
|
|
|
|
676
|
100
|
|
|
|
|
|
|
|
1992-2000
|
Forest
|
Mechanically
disturbed
|
379
|
42
|
|
|
Mechanically
disturbed
|
Forest
|
362
|
40
|
|
|
Forest
|
Mining
|
56
|
6
|
|
|
Forest
|
Developed
|
27
|
3
|
|
|
Non-mechanically
disturbed
|
Forest
|
26
|
3
|
|
|
Other
classes
|
Other
classes
|
48
|
5
|
|
|
|
|
898
|
100
|
|
Overall:
|
|
|
|
|
|
1973-2000
|
Forest
|
Mechanically
disturbed
|
1,055
|
39
|
|
|
Mechanically
disturbed
|
Forest
|
928
|
34
|
|
|
Forest
|
Mining
|
174
|
6
|
|
|
Non-mechanically
disturbed
|
Forest
|
110
|
4
|
|
|
Forest
|
Non-mechanically
disturbed
|
108
|
4
|
|
|
Other
classes
|
Other
classes
|
355
|
13
|
|
|
|
|
2,730
|
100
|

Figure 1. North Central
Appalachians and surrounding ecoregions. The 10 randomly selected 400-km²
sample blocks are shown along with land use/land cover from the 1992 National
Land Cover Dataset.

Figure 2. Predominately
forested area with scattered agriculture.

Figure 3. Pennsylvania Fish
and Boat Commission Tidioute recreation area along the Allegheny River

Figure 4. The overall
spatial change in all Eastern U.S. ecoregions. Each bar chart shows the
proportion of the ecoregion that experienced change on 1, 2, 3, or 4 dates.

Figure 5. The estimates of
land cover change per time interval normalized to an annual rate of change.
North Central Appalachian ecoregion is highlighted in black.

Figure 6. Per period net
change for each land cover class. Areas above zero represent net gains for a
land cover class, while areas below represent a net loss.

Figure 7. Small sawmill 10
miles northwest of Port Jervis, New York.

Figure 8. Modular homes
waiting to be transferred to housing site.