Northeastern Highlands
By Steve Kambly 1
Click to see available downloads for this ecoregion

Figure 1. The Northeastern Highlands and surrounding ecoregions. The randomly selected sample blocks are shown along with land use/land cover data from the 1992 National Land Cover Dataset. Click to enlarge.
Ecoregion Description
The Northeastern Highlands ecoregion consists of four
physically separate areas, which occupy 127,109 km2 (49,077 mi2)
in Maine, New Hampshire, Vermont, New York, Massachusetts, Connecticut, New Jersey, and Pennsylvania (fig. 1). The ecoregion is “a relatively sparsely populated
region characterized by nutrient poor soils blanketed by northern hardwood and
spruce fir forests. Land-surface form in the region grades from low mountains
in the southwest and central portions to open high hills in the northeast”
(U.S. Environmental Protection Agency, 2002). Numerous mountain ranges,
including the White Mountains in New Hampshire, the Green Mountains in Vermont, and New York’s Catskills and Adirondacks, lie within the ecoregion. The ecoregion
also shows many remnants of glaciation, including rocky soils, glacial lakes,
and wetlands (fig. 2). Annual average rainfall varies from 940 to 1,397 mm (37
to 55 in), with significantly higher amounts in mountainous areas. The average
daily temperature ranges from below –7oC (20o F) in
January to between 16 and 21oC (60 and 70oF) in July.
Though the ecoregion was heavily forested at the beginning
of European settlement, much of it was cleared for farmland in the 19th
century. Farmland abandonment, beginning in the mid-1800s and continuing
through the study period, has led to a natural regrowth of forest. Forest
harvesting for wood products has been an ongoing activity since the early
1800s—and clear-cutting of forest was evident during the study period in
western Maine, where timber companies control large tracts of land. Paper and
pulp processing is the leading manufacturing activity in Maine. Further south,
in New Hampshire, Vermont, and New York, tourism and small-scale farming are
more prevalent.
Change from 1973 to 2000
A moderate amount of change was
observed in the Northeastern Highlands ecoregion, with an estimated 8.9 percent
of its area converting to another land cover at least once during the study
period (fig. 3). Approximately 3.1 percent changed only once, while 3.6
percent and 2.1 percent changed two and three times, respectively. About
one-tenth of 1 percent of the ecoregion’s area was converted four times. Of
the thirty-five sample blocks in the ecoregion, five blocks in western Maine had rates of change exceeding 25 percent. The high rates of change were due
primarily to forest clear-cutting and regrowth (fig. 4). Thirteen blocks had
less than 2 percent change, most of which fell within State or Federally owned
lands such as parks, forests, or refuges where forestry practices are
restricted or disallowed altogether (fig. 5). Total change per interval
increased from 2.3 percent between 1973 and 1980 to 6.2 percent between 1992
and 2000 (
). Average annual rates of change increased steadily in the
first three intervals from 0.3 percent to 0.9 percent and then slowed to 0.8
percent between 1992 and 2000 (fig. 6).
Forest harvesting and regrowth was the dominant pattern of change observed.
Both the selective cutting and clear-cutting of forest created mechanically
disturbed lands, which in turn became grassland/shrubland. Eventually,
grassland/shrubland areas tended to become re-forested. This cycle of change,
in which mechanically disturbed lands and grassland/shrubland are transitional
land covers, occurred over an increasing area between 1973 and 1992, but
contracted in the last interval.
Primarily as a result
of clear-cutting and some selective harvesting, forest decreased by an
estimated 3.8 percent (table 2) or approximately 4,830 km2 (1,865 mi2).
However, forest remained the dominant land cover, extending over an estimated
81.4 percent of the ecoregion in 2000. As the amount of tree harvesting
increased, the percent of mechanically disturbed land also increased—from 0.6
percent in 1973 to 2.1 percent in 2000. The amount of estimated land area in
grassland/shrubland increased between 1973 and 1992 from 0.2 percent to 2.2
percent and then decreased slightly in the last interval to 2.1 percent.
Developed land increased from 1.8 percent to 2.3 percent between 1973 and 2000,
while farmland remained unchanged with approximately 3.3 percent of the
ecoregion’s land area. Forest, mechanically disturbed land, and
grassland/shrubland were by far the most active land covers, accounting for
most of the net change in the ecoregion during the study period (fig. 7).
In terms of individual conversions, forest to mechanically
disturbed land was the most common conversion overall, as well as in the first
three intervals (table 3). An estimated 9,322 km2 (3,603 mi2)
converted from forest to mechanically disturbed land between 1973 and 2000.
The second most common conversion both overall and in each interval was
mechanically disturbed land to grassland/shrubland with 6,983 km2
(2,696 mi2) in conversions. Grassland/shrubland to forest was the
third most common conversion. Approximately 4,641 km2 (1,792 mi2)
of land area converted from grassland/shrubland to forest during the study
period.
While 150 years of farmland abandonment has led to regrowth
of forests in the Northeastern Highlands, forest harvesting was clearly the
dominant type of land cover change between 1973 and 2000. Strong demand for
forest products spurred timber companies to harvest vast tracts of forested
land in sparsely populated regions of central and northern Maine. State and
Federally owned reserved lands, however, may have played a role in limiting
forest harvesting. Farming was scattered and generally small-scale in the
ecoregion and did not change significantly during the study period (fig. 8).
The amount of developed land did increase slightly, in the form of new
residential communities and tourist resorts, primarily due to conversion of
forested land.
References
Colgan, C.S., Irland, L.C., and Benson, J., 1986, The
natural resource industries of Maine—An assessment and statistical portrait: Augusta: Financial Authority of Maine and Maine State Planning Office.
Hart, John Fraser, 1968,
Loss and abandonment of cleared farm land in the Eastern United States: Annals
of the Association of American Geographers, v. 58, no. 5, p. 417–440.
Irland, L.C., 1999, The Northeast’s changing forest: Petersham, Mass., Harvard Forest [distributed by Harvard University Press], 427 p.
Prescott, Richard, and Vail, David,
1988, The transformation of farming in Maine, 1940–1985: Maine Historical
Quarterly, v. 28, p. 66–84.
U.S. Environmental Protection
Agency, 2002, Primary distinguishing characteristics of Level III ecoregions of
the continental United States [draft]: EPA, available online at
ftp://ftp.epa.gov/wed/ecoregions/us/useco_desc.doc.
Table 1. Change per time
period
|
|
Period
|
|
|
1973–1980
|
1980–1986
|
1986–1992
|
1992–2000
|
|
Total
change (% of ecoregion)
|
2.3%
|
3.9%
|
5.5%
|
6.2%
|
|
Margin of
error (85% confidence level)
|
+/–1.3%
|
+/–1.7%
|
+/–2.1%
|
+/–2.4%
|
|
Average
annual rate of change (%/year)
|
0.3%
|
0.7%
|
0.9%
|
0.8%
|
Table 2. Percent change per
interval by category
|
|
1973
|
1980
|
1986
|
1992
|
2000
|
Net change 1973–2000
|
|
Land-use/land-cover
class
|
km²
|
%
|
km²
|
%
|
km²
|
%
|
km²
|
%
|
km²
|
%
|
km²
|
%
|
|
Water
|
6,487
|
5.1
|
6,482
|
5.1
|
6,500
|
5.1
|
6,516
|
5.1
|
6,496
|
5.1
|
9
|
0.0
|
|
Developed
|
2,317
|
1.8
|
2,420
|
1.9
|
2,499
|
2.0
|
2,674
|
2.1
|
2,949
|
2.3
|
632
|
0.5
|
|
Mechanically
disturbed
|
773
|
0.6
|
1,716
|
1.4
|
2,532
|
2.0
|
2,553
|
2.0
|
2,622
|
2.1
|
1,849
|
1.5
|
|
Mining
|
65
|
0.1
|
77
|
0.1
|
85
|
0.1
|
104
|
0.1
|
122
|
0.1
|
56
|
0.0
|
|
Naturally
barren
|
142
|
0.1
|
142
|
0.1
|
142
|
0.1
|
142
|
0.1
|
142
|
0.1
|
0
|
0.0
|
|
Forest
|
108,325
|
85.2
|
106,703
|
83.9
|
104,564
|
82.3
|
103,672
|
81.6
|
103,421
|
81.4
|
–4,904
|
–3.9
|
|
Grassland/Shrubland
|
243
|
0.2
|
852
|
0.7
|
2,090
|
1.6
|
2,768
|
2.2
|
2,688
|
2.1
|
2,445
|
1.9
|
|
Agriculture
|
4,210
|
3.3
|
4,165
|
3.3
|
4,165
|
3.3
|
4,157
|
3.3
|
4,160
|
3.3
|
–51
|
0.0
|
|
Wetland
|
4,546
|
3.6
|
4,553
|
3.6
|
4,532
|
3.6
|
4,523
|
3.6
|
4,500
|
3.5
|
–46
|
0.0
|
|
Non-mechanically
disturbed
|
0
|
0
|
0
|
0
|
0
|
0.0
|
0
|
0.0
|
0
|
0.0
|
0
|
0.0
|
Table 3. Leading conversions by interval and for the entire
study period
|
|
|
|
Area changed
|
% of all
|
|
Period
|
From
class
|
To
class
|
(km2)
|
changes
|
|
1973–1980
|
Forest
|
Mechanically
disturbed
|
1,715
|
60
|
|
|
Mechanically
disturbed
|
Grassland/Shrubland
|
724
|
25
|
|
|
Grassland/Shrubland
|
Forest
|
127
|
4
|
|
|
Forest
|
Developed
|
85
|
3
|
|
|
Agriculture
|
Forest
|
80
|
3
|
|
|
Other
classes
|
Other
classes
|
132
|
5
|
|
|
|
|
2,863
|
100
|
|
|
|
|
|
|
|
1980–1986
|
Forest
|
Mechanically
disturbed
|
2,519
|
50
|
|
|
Mechanically
disturbed
|
Grassland/Shrubland
|
1,684
|
34
|
|
|
Grassland/Shrubland
|
Forest
|
481
|
10
|
|
|
Forest
|
Agriculture
|
81
|
2
|
|
|
Forest
|
Developed
|
67
|
1
|
|
|
Other
classes
|
Other
classes
|
179
|
4
|
|
|
|
|
5,010
|
100
|
|
|
|
|
|
|
|
1986–1992
|
Forest
|
Mechanically
disturbed
|
2,517
|
36
|
|
|
Mechanically
disturbed
|
Grassland/Shrubland
|
2,266
|
32
|
|
|
Grassland/Shrubland
|
Forest
|
1,619
|
23
|
|
|
Mechanically
disturbed
|
Forest
|
244
|
3
|
|
|
Forest
|
Developed
|
161
|
2
|
|
|
Other
classes
|
Other
classes
|
213
|
3
|
|
|
|
|
7,020
|
100
|
|
|
|
|
|
|
|
1992–2000
|
Forest
|
Mechanically
disturbed
|
2,571
|
32
|
|
|
Grassland/Shrubland
|
Forest
|
2,413
|
30
|
|
|
Mechanically
disturbed
|
Grassland/Shrubland
|
2,309
|
29
|
|
|
Forest
|
Developed
|
194
|
2
|
|
|
Mechanically
disturbed
|
Forest
|
160
|
2
|
|
|
Other
classes
|
Other
classes
|
278
|
4
|
|
|
|
|
7,925
|
100
|
|
Overall:
|
|
|
|
|
|
1973–2000
|
Forest
|
Mechanically
disturbed
|
9,322
|
41
|
|
|
Mechanically
disturbed
|
Grassland/Shrubland
|
6,983
|
31
|
|
|
Grassland/Shrubland
|
Forest
|
4,641
|
20
|
|
|
Forest
|
Developed
|
506
|
2
|
|
|
Mechanically
disturbed
|
Forest
|
454
|
2
|
|
|
Other
classes
|
Other
classes
|
912
|
4
|
|
|
|
|
22,818
|
100
|

Figure 1. The Northeastern Highlands and surrounding ecoregions. The randomly selected sample blocks
are shown along with land use/land cover data from the 1992 National Land Cover
Dataset.

Figure 2. The many wetlands
in the ecoregion are a result of glaciation.

Figure 3. 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
4. Most landcover change in the ecoregion is the result of extensive
clear-cutting in Maine.

Figure 5. Reserved lands
such as Adirondack State Park place restrictions on timber harvesting and
development.

Figure 6. Estimates
of land cover change per time interval normalized to annual rates of change.
Figure 7. Net land cover changes
by categories for each time interval and for the entire study period.

Figure 8. Although there are
many prosperous farms in the ecoregion, generally agriculture is in decline.