Putnam Uplands
Land Type
Association (LTA) 221 Ae 06

Figure 3-30. Low relief landscape, Putnam County, New York. Photo by Jeff Wiegert.
This LTA lies
wholly within New York State. It is
characterized by rolling hills and ridges.
The landscape is much less rugged than that in the adjacent New York
Hudson Highlands due to the infilling of valleys with glacial till during the
Wisconsinan glaciation.
Most
of the landscape is covered with glacial till deposits that are deepest in
major valleys. Sand and gravel outwash
deposits, kames, swamps and bedrock occur but to a minor extent. Mid-slope rock outcrops including cliff and
talus formations are more common than the rocky balds that are typical of the
New York Hudson Highlands LTA.
The
Putnam Uplands LTA lies in the Croton/Hudson drainage basin but these major
rivers lie outside the units. Most of
the streams within the Putnam Uplands are headwater and small tributary
streams.
The
soils include very deep, well-drained loamy soils as well as moderately deep to
shallow, excessively drained coarse-textured soils. The nearly level valleys are largely occupied by more fertile
well-drained loamy soils that formed in sub glacial till. These soils are very deep to bedrock but
moderately deep to a densic contact.
Soils series include Paxton, Woodbridge, Charlton, Hollis, and
Chatfield.

Figure 3-31. Location map of LTA 221 Ae 06.
About a third of the
land in the LTA is upland forest.
Another 7% is wetland forest.
Vegetation in the Putnam Uplands resembles that of the Rockaway
Highlands. Ridgetop barrens are rare,
oak-dominant forests occupy dry hills and upper slopes, and maple-dominant
forests prevail in valleys and on lower slopes. Deep fertile till soils support a diversity of common trees. Any of the following may be co-dominant in
the tree canopy of the forest communities: northern red oak, white oak, black
oak, chestnut oak, sugar maple, red maple, white ash, and American elm. Less common, but widespread are tuliptree,
American beech, pignut hickory, bitternut hickory and white pine. Sassafras, basswood, black gum, shagbark
hickory and eastern hemlock are found locally in special habitats.
Almost half the land in this LTA is developed. There is only a small amount of agricultural land.
Figure 3-32. Oak forest,
Putnam County, New York. Photo by
Jeff Weigert.
New
York Highlands Valleys

Land Type Association (LTA) 221 Ae 07
Figure 3-34. Ramapo River near Sloatsburg, New York. Photo by Arlene Miller.
The New York Highlands Valleys land type
association consists of multiple occurrences of valleys, gorges and ravines
that dissect the New York Hudson Highlands LTA 221 Ae 05. The Moodna Creek, Ramapo River and Mahwah
River valleys comprise one unit. There
are five smaller valleys east of the Hudson River. New York State Route 9 runs along Clove Creek Valley, which drains
north from the north rim of the Hudson Highlands into the Hudson Valley
subsection (221 Ba) in the Town of Fishkill.
Canopus Brook Valley and Peekskill Hollow Valley descend southwest to
converge, merge, and enter Annesville Creek flowing into the Hudson River. The Muddy Brook and Upper East Branch Croton
River Valleys dissect the Northern Highlands ridge near the Connecticut
boundary. The Upper East Branch Croton
River Valley contains the Great Swamp, the largest contiguous wetland area in
the greater New York Hudson Highlands.
The Muddy Brook and Upper East Branch Croton River Valleys dissect the
Northern Highlands ridge near the Connecticut boundary. The Upper East Branch Croton River Valley
contains the Great Swamp, the largest contiguous wetland area in the greater
New York Hudson Highlands.
Glacially derived parent materials, primarily outwash sand and gravel, till, kame deposits and recent alluvium, characterize the LTA.

Figure 3-35. Location map of LTA 221 Ae 07.
Soils formed in outwash tend to be very deep and somewhat excessively drained soils. Soils formed in till are more likely to be well-drained loamy soils. Soil series include Hoosic, Windsor, Limerick, Charlton, Hollis, Chatfield and Limerick.
Half of this LTA is forestland and most of it is upland forest (45%). The most common trees are mesophytes such as sugar maple, black oak, white ash, American beech, basswood, tuliptree, bitternut hickory and white pine, or species with a wide moisture tolerance such as red maple, northern red oak, white oak, and eastern hemlock. These valleys contain limited areas of floodplain or swampland, with characteristic trees such as silver maple, ash-leaf maple, green ash, cottonwood, basswood and sycamore. Spicebush and northern arrow wood are common under story shrubs. Although forest associations prevail, there are also areas of shrub swamp and shallow marsh along the floodplains of major streams. The Great Swamp valley unit in eastern Putnam Country contains a very large (approximately 6,000 acres) and diverse wetland complex, draining north into the Housatonic River watershed, and south into the Croton River watershed. Thus the Great Swamp valley is critical to a number of local and municipal water supplies, including that of New York City (Croton Reservoir).

Almost a third of this LTA is developed land.
There is limited agricultural activity.
All of the valleys have a long history of use as transportation
corridors. The Ramapo Valley is
traversed by both the New York State Thruway and New York State Route 17. The Peekskill Hollow and Canopus Brook
Valleys are the least disturbed.
Figure 3-37. Alluvial plain
on the Ramapo River. Photo by
Martina Hoppe, 2003.
Photo by Martina Hoppe

Parker-Edneyville Highlands
Land Type Association (LTA) 221 Am 01

Figure 3-38. Fractured bedrock in South Branch of Raritan River, Ken Lockwood Gorge, Hunterdon County, New Jersey. Photo by Dave MacFarlane.
The Parker-Edneyville Highlands land type
association includes portions of the New Jersey Highlands, south of the
terminal moraine of the Wisconsinan glacier, where soils are derived from
deeply weathered fragments of gneiss rock.
The landscape is characterized by broad mountains, which are subdivided
into northeast-southwest trending belts by deep, narrow valleys. Some of the mountain belts are deeply
dissected into and crosscut by narrow gorges, creating clusters of “hilly”
mountains. Toe-slopes, foothills and
the drainages of mountain streams are mostly filled with transported colluvium
(fractured bedrock) and residuum (old glacial till) from the Kansan and
Illinoian glaciers.
The LTA includes the headwaters of the Raritan, Upper Delaware, and Passaic drainage basins. Lakes, ponds and reservoirs make up only a small portion of these highlands.

Figure 3-39. Location map of LTA 221 Am 01.
The soils of these highlands are generally deep and stony and have been deeply weathered, unlike soils in the New York–New Jersey Highlands to the north. Substantial weathering of the generally mineral-rich gneiss rock moderates what would otherwise be generally poor, acidic mountain soil. Soils are generally well drained, although the coarse texture of the soils and steep topography create excessively drained conditions in many places. Impeded drainage is also much less common on uplands that it is in the Rockaway Highlands to the north, where glacial compacted materials in the subsoil trap percolating rainwater. In the Parker-Edneyville Highlands, most of the areas with impeded drainage occur on upland flats, toe slopes, drainage ways and depressions that contain deeply weathered old glacial till, or in other areas where compacted materials are present in the subsoil. Major soil series include park Edneyville, Annandale, Califon and Cokesbury.
Natural plant communities cover a substantial portion of these highlands. Most of these are upland forests (54%) that have regenerated on fallow agricultural land or cutover timberland. Forested wetlands make up a minor portion of the landscape. Common forest trees include a diverse mixture of white oak, black oak, northern red oak, sugar maple, American beech, black birch, red maple, white ash, sassafras, and tulip tee. Tulip tree was the most abundant species in many places, probably because of the abundance of deep, well-drained mountain soils found throughout the LTA. Red maple and white ash are most common on wet, rocky flats. Chestnut oak and scarlet oak are sometimes common hilltops and rocky plateaus.

Basswood, shagbark
hickory, yellow birch, black gum, and American elm are somewhat common,
particularly on rocky flats and gentle slopes where drainage is impeded by a
fragipan. Pignut, butternut and
mockernut hickory are sometimes present on slopes a hilltops. Eastern hemlock is scattered throughout,
mainly occurring on steep shady slopes and in the forest under story.
Agriculture is still common accounting for
about 13% of all land use. Nearly a
quarter of the land in Parker-Edneyville Highlands LTA is developed, primarily
for residential purposes.
Musconetcong and Upper Raritan Valleys
Land Type Association (LTA) 221 Am 02

Figure 3-42. A farm in Long Valley on a well-drained limestone till slope. Photo reprinted from MacFarlane and Dunn, 2002.
The Musconetcong and Upper Raritan Valleys
land type association includes a number of large and small valleys, gorges and
ravines that dissect the Reading Prong Subsection. A mixture of, primarily, young (Wisconsinan) and old (Kansan and
Illinoian) glacial drift deposits and frost-worked colluvium from surrounding
limestone and gneiss bedrock cover the valley.
More recently deposited alluvial materials are present along the
floodplains of rivers and streams. In
some places, outcrops of bedrock are present, including a few small
ridges. Glacial drift deposits in the
valleys have been worked and reworked over long time periods creating a rolling
“hill and hollow” topography in the valleys.
A limited “karst topography” consisting of sinks, underground streams
and caverns, has developed in some of the limestone formations.
The Musconetcong Valley is dominated by limestone bedrock, which the Musconetcong River was able to wear away over time (this material is softer than the hard gneiss rock of the parker-Edneyville Highlands that surrounds it). Surface materials consist mostly of limestone till and colluvium, which are variably mixed with gneiss till and stratified gneiss drift. The Musconetcong River flows through the Musconetcong valley out into the Delaware River. Long Valley, the largest of the Upper Raritan Valleys, is similar geologically to the Musconetcong, while the rest of them are dominated primarily by gneiss drift materials. The South Branch Raritan River flows through Long Valley, eventually joining the main body of the Raritan River, which flows into the Raritan Bay.

Figure 3-43. Location map of LTA 221 Am 02.
The Black River, Lamington River and North Branch Raritan River, flow through the other smaller valleys, and also eventually flow into the main body of the Raritan River. In some places, where streams have carved directly through gneiss bedrock, these valleys are quite narrow.
The soils in this LTA are a mixture of stratified silty or sandy loams (mixed frequently with stones and gravel), limestone and gneiss till and alluvial soils. These soils developed in glacial till and drift scoured from local bedrock or transported by glacial outwash streams. Beds of stratified silt and clay are sometimes common on lowland plains, where glacial lakes once stood, impeding soil drainage. In many areas, soils naturally enriched with calcium and magnesium, from dolomitic limestone, chert and marble or fossilized organic materials (found in carbonaceous rock formations). Major soil series include Hero, Hazen, Fredon, Halsey, Bartley, Duffield, Washington, Turbotville, Otisville, Riverhead, Pompton, Preakness, Carlisle and Adrian.

Natural plant communities cover less than a third of the landscape in the LTA,
most of which have regenerated on fallow farmland. Forests comprise over a fifth of the landscape, upland forests
are most extensive (16%) than wetland forests (6%). Upland forests are found mostly on steep hillsides or rocky
limestone ledges. These are mostly
young woodlands consisting mainly of black cherry, red maple, aspen, gray birch
and eastern red cedar, along with occasional dense populations of black locust
and ailanthus. Common trees in mature
forests include a diverse mixture of tulip tree, white ash, red maple, sugar
maple, black birch, American beech, northern red oak, white oak, yellow
birch, American elm,
black oak, shagbark hickory, black gum, pignut hickory, mockernut hickory,
bitternut hickory, black walnut, and basswood.
Chestnut oak, scarlet oak and white pine are occasionally present but
are mostly limited to hilltops or exceptionally sandy and gravelly stream
terraces. Flowering dogwood, iron wood
and sassafras are common under story trees throughout. Forested wetlands
(swamps) cover a small part of the landscape.
Pin
oak, swamp white oak, yellow birch, and black
gum are all common trees in swamps, which occur mainly on low-lying river
terraces and on floodplains, along the courses of rivers and streams. Sycamore, river birch, elm and green ash are
abundant along stream banks and on floodplains. Non-forested natural plant communities cover a substantial
portion of the landscape, including large areas of shrub and grassland
communities, which have developed on more recently abandoned agricultural lands
and large areas of freshwater marshlands, shrub-marshes and peaty meadows.
The generally deep, rich soils
of these valleys have been farmed for a long time and over a third of the land
is cultivated. About 29% is developed
land.
3-3.
References
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Lauber, L.V. Rickard, and W.B. Rogers, editors. 1991. Geology of New York, a
Simplified Account. New York State
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12230, 1991. 265 pages.
Keys, Jr., J. Carpenter, C.; Hooks, S.; Koenig, F.; McNab, W.H.; Russell, W.; Smith, M.L. 1995. Ecological units of the eastern United States–first approximation (map and booklet of map unit tables), Atlanta, GA: U.S. Department of Agriculture, Forest Service. Presentation scale 1:3,500,000; colored.
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20th Ed., publ. John Wiley & Sons.
Kuchler, A.W. 1964. Potential natural vegetation of the conterminous United States. Special Publication 36. New York, NY: American Geographical Society 116 p.
Lundgren, Julie A. (ed.) 2000. Plant communities of the Lower New England –Northern Piedmont Ecoregion June 2000. The Nature Conservancy Conservation Science Eastern Region. Boston, MA Adapted from: Sneddon, L., Anderson, M.; and Lundgren, J.; 1998. International classification of ecological communities: Terrestrial vegetation of the northeastern United States. January 1999 working draft. Association for Biodiversity Information/The Nature Conservancy, Eastern Resource Office, and Natural Heritage Programs of the Northeastern United States. Boston. MA.
Lundgren, J.A. 2001. Plant Communities of the High Allegheny Plateau Ecoregion: Draft Revisions to the National Vegetation classification 3/2000 subset. Natural Heritage Central Databases. The Association for Biodiversity Information, Arlington, VA and The Nature Conservancy–Eastern Regional Office, Boston, MA. 71 pages plus appendixes.
MacFarlane, Dave and James Dunn
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Phelps, M.G. and M. C. Hoppe (compilers) 2002. New York–New Jersey Highlands Regional Study: 2002 Update. NA-TP-02-03. United States Department of Agriculture, Forest Service Northeastern Area State and Private Forestry, Newtown Square, PA.
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Appendix 3-A. Land Aspect
Table 3-A. Distribution (acres) of land by aspect for Land Type Associations in the New York–New Jersey Highlands Subsection 221 Ae and the Reading Prong Subsection 221 Am (NYS DEC 2000).
LTA
|
Ae 01 |
Ae 02 |
Ae 03 |
Ae 04 |
Ae 05 |
Ae 06 |
Ae 07 |
Am 01 |
Am 02 |
|
Aspect |
|
||||||||
|
Flat |
3,569 |
23,660 |
7,564 |
166 |
41,734 |
5,460 |
6,328 |
1,144 |
2,655 |
|
North |
14,445 |
120,002 |
30,562 |
5,490 |
118,222 |
8,037 |
7,439 |
107,565 |
31,696 |
|
Northeast |
11,448 |
109,092 |
22,292 |
2,729 |
110,275 |
9,972 |
8,257 |
73,966 |
21,845 |
|
East |
29,395 |
180,826 |
32,258 |
3,312 |
191,833 |
26,133 |
15,108 |
113,915 |
38,687 |
|
Southeast |
40,009 |
207,025 |
39,728 |
8,712 |
199,504 |
15,258 |
14,444 |
187,561 |
70,874 |
|
South |
14,234 |
123,169 |
24,969 |
5,043 |
117,386 |
10,619 |
5,929 |
130,761 |
53,320 |
|
Southwest |
12,465 |
104,466 |
21,503 |
2,634 |
110,555 |
12,465 |
6,602 |
85,202 |
38,359 |
|
West |
29,173 |
180,223 |
33,803 |
4,325 |
193,983 |
25,005 |
18,074 |
108,368 |
48,454 |
|
Northwest |
47,202 |
212,412 |
53,981 |
9,573 |
198,633 |
14,587 |
17,511 |
170,762 |
56,555 |
Table 3-B. Distribution (acres) of land by percent slope for Land Type
Associations (LTA) in the New York–New Jersey Highlands Subsection 221 Ae and
Reading Prong Subsection 221 Am (NYS DEC 2000).
|
LTA |
Ae 01 |
Ae 02
|
Ae 03 |
Ae 04 |
Ae 05 |
Ae 06 |
Ae 07 |
Am 01 |
Am 02 |
|
Slope |
|
||||||||
|
0-6 % |
58,002 |
388,107 |
155,689 |
4,385 |
268,285 |
56,691 |
44,751 |
283,767 |
252,419 |
|
6-12 % |
53,487 |
348,260 |
67,337 |
8,877 |
285,555 |
39,717 |
23,015 |
333,625 |
82,173 |
|
12-24 % |
56,676 |
376,941 |
38,267 |
15,625 |
433,331 |
27,498 |
22,472 |
281,361 |
24,534 |
|
24-36 % |
21,277 |
107,346 |
4,775 |
8,309 |
190,080 |
3,111 |
7,045 |
64,390 |
2,828 |
|
36-60 % |
11,434 |
37,409 |
584 |
4,397 |
93,179 |
511 |
2,255 |
15,562 |
486 |
|
60-84 % |
1,003 |
2,650 |
8 |
364 |
10,171 |
8 |
173 |
526 |
5 |
|
>84 % |
41 |
162 |
- |
27 |
1,520 |
- |
11 |
13 |
- |
Appendix 3-C. Elevation
Table 3-C. Distribution (acres) of land by elevation class for Land Type Associations (LTA) in the New York–New Jersey Highlands Subsection 221 Ae and Reading Prong Subsection 221 Am (NYS DEC 2000).
|
LTA |
Ae 01
|
Ae 02 |
Ae 03 |
Ae 04 |
Ae 05 |
Ae 06 |
Ae
07
|
Am 01 |
Am 02 |
|
Elevation |
|
||||||||
|
0–200 feet |
0 |
471 |
287 |
0 |
54,362 |
1,264 |
6,633 |
896 |
7,830 |
|
200–400 feet |
2,408 |
66,080 |
14,133 |
8 |
81,567 |
19,193 |
31,603 |
65191 |
161,688 |
|
400–600 feet |
19,746 |
164,129 |
118,887 |
6,930 |
238,965 |
74,755 |
45,859 |
225,993 |
128,073 |
|
600–800 feet |
60,523 |
296,131 |
105,078 |
16,130 |
343,380 |
31,762 |
14,426 |
316,229 |
58,974 |
|
800–1,000 feet |
53,614 |
341,740 |
26,349 |
14,804 |
332,362 |
562 |
1,170 |
272,332 |
5,704 |
|
>1,000 feet |
65,649 |
392,324 |
1,926 |
4,112 |
231,280 |
- |
1 |
98,603 |
176 |
Appendix
3-D. Bedrock
Table 3–D. Distribution (acres) of land by bedrock composition for Land Type Associations (LTA) in the New York–New Jersey Highlands Subsection 221 Ae and Reading Prong 221 Am. (N.J. Geological Survey 2000; NYS Museum / NYS Geological Survey 1992).
LTA
|
Ae 01 |
Ae 02
|
Ae 03 |
Ae 04 |
Ae 05 |
Ae 06 |
Ae 07 |
Am 01 |
Am 02 |
|
Bedrock |
|
||||||||
Amphibolite
|
110 |
12,668 |
1,127 |
143 |
56,051 |
- |
3,971 |
10,857 |
1,405 |
|
Basalt |
- |
- |
255 |
- |
- |
- |
- |
- |
- |
|
Conglomerate |
18,439 |
6.617 |
982 |
- |
- |
- |
2,098 |
2,282 |
1,508 |
|
Dolostone |
- |
5,198 |
18,104 |
250 |
6,715 |
- |
9,602 |
19,629 |
55,996 |
|
Gneiss |
5,953 |
141,820 |
13,639 |
5,494 |
209,722 |
25,798 |
9,675 |
83,119 |
7,069 |
|
Granite |
2,582 |
89,431 |
6,981 |
3,169 |
- |
1,296 |
- |
87,483 |
4,155 |
|
Limestone |
335 |
- |
523 |
- |
- |
- |
- |
- |
2,960 |
|
Marble |
- |
4,649 |
5,113 |
264 |
- |
542 |
1,622 |
- |
441 |
|
Phyllite/Schist |
- |
- |
- |
- |
2,770 |
- |
639 |
- |
- |
|
Quartzite |
- |
- |
- |
- |
2,304 |
614 |
- |
- |
- |
|
Sandstone |
5,088 |
4,176 |
2,442 |
114 |
- |
- |
- |
3,582 |
1,622 |
|
Shale |
2,918 |
3,140 |
2,112 |
- |
- |
- |
- |
- |
9,902 |
|
Ultramafic |
- |
21,275 |
- |
- |
- |
- |
- |
22,747 |
- |
|
Unconsolidated sediments |
- |
- |
- |
- |
- |
- |
271 |
- |
- |
Appendix
3-E. Surficial Geology
Table 3-E. Distribution (acres) of land by surface geology class for Land Type Associations (LTA) in the New York–New Jersey Highlands 221 Ae and Reading Prong 221 Am.
LTA
|
Ae 01 |
Ae 02 |
Ae 03 |
Ae 04 |
Ae 05 |
Ae 06 |
Ae 07 |
Am 01 |
Am 02 |
|
|
Surface geology |
|
|||||||||
|
Thin till and rock outcrop* |
17,838 |
159,954 |
8,857 |
6,752 |
54,371 |
404 |
1,094 |
29 |
- |
|
|
Till** |
22,818 |
81,855 |
17,687 |
677 |
215,152 |
25,897 |
6,466 |
339 |
59 |
|
|
Glaciofluvial and glacio-lacustrine deposits*** |
2,838 |
18,132 |
22,448 |
153 |
1,611 |
748 |
7,264 |
2,677 |
9,036 |
|
|
Ice contact deposits**** |
1,035 |
4,208 |
1,284 |
- |
5,361 |
639 |
2,849 |
- |
- |
|
|
Morainic deposits |
30 |
12,820 |
5,150 |
421 |
- |
- |
- |
3,099 |
286 |
|
|
Alluvial, colluvial, and weathered bedrock***** |
190 |
3,814 |
1,288 |
1,313 |
880 |
5 |
2,726 |
203,410 |
59,184 |
|
|
Swamp deposits |
135 |
- |
951 |
- |
473 |
660 |
- |
- |
- |
|
|
Pre-Wisconsin Age till+ |
- |
- |
- |
- |
- |
- |
- |
7,311 |
11,406 |
|
|
Pre-Wisconsin Age glacio-fluvial and glaciolacustrine deposits++ |
- |
- |
- |
- |
- |
- |
- |
823 |
590 |
|
|
TOTAL |
44,884 |
|
57,665 |
9,316 |
277,848 |
28,353 |
20,399 |
217,688 |
80,561 |
|
* Combined categories: thin till
and rock outcrop in New Jersey; bedrock in New York.
**
Combined categories: continuous till, in New Jersey; till in New York.
*** Combined categories: deltaic and lacustrine-fan,
fluvial over lacustrine, lake-bottom, and fluvial deposits in New Jersey;
outwash sand and gravel in New York.
****
Combined categories: ice contact deposits in New Jersey; kame deposits in New
York.
*****Combined
categories: colluvial and alluvial deposits and weathered bedrock material in
New Jersey with recent alluvium and alluvial fan in New York.
+
Combined categories: till (Illinoian
age), till (Jerseyan age), morainic deposits (Illinoian) in New Jersey.
++ Combined categories: deltaic and lacustrine fan
(Illinoian), fluvial and deltaic (Jerseyan), fluvial (Illinoian) in New Jersey.
Appendix 3-F. New York–New Jersey Highlands Region 200 Level 3 Land Cover Data.
Table 3-F. Distribution (percent) of land cover and land use for Land Type Associations (LTA) in the New York–New Jersey Highlands Subsections 221 Ae and the Reading Prong Subsection 221 Am (CRSSA 2002).
LTA
|
Ae 01 |
Ae 02 |
Ae 03 |
Ae 04 |
Ae 05 |
Ae 06 |
Ae 07 |
Am 01 |
Am 02 |
Categories*
|
|
|
|
|
|
|
|
|
|
Developed land
|
17 |
17 |
29 |
6 |
13 |
49 |
31 |
24 |
29 |
|
Cultivated land |
2 |
1 |
13 |
3 |
1 |
3 |
5 |
13 |
38 |
|
Grassland |
1 |
1 |
6 |
4 |
1 |
2 |
3 |
3 |
6 |
|
Upland forest |
69 |
67 |
31 |
85 |
75 |
33 |
45 |
54 |
16 |
|
Barren soil/rock |
0 |
1 |
1 |
0 |
1 |
0 |
1 |
0 |
1 |
|
Riverine / lacustrine / palustrine |
1 |
1 |
7 |
0 |
1 |
1 |
3 |
1 |
2 |
|
Wetland forest |
5 |
7 |
10 |
1 |
3 |
7 |
7 |
4 |
6 |
|
Open water |
5 |
5 |
3 |
1 |
5 |
5 |
5 |
1 |
2 |
* Categories are groups of remotely sensed classes described below.
Categories/Classes collapsed for use in the section.
111 Developed: highly (>75% impervious surface)
112 Developed: moderately (50-75% impervious surface)
113 Developed: lightly-wooded (25-50% impervious surface)
114 Developed: lightly – not wooded (25-50% impervious surface)
120 Cultivated (actively tilled, fallow and recently abandoned)
131 Grassland: unmanaged (grazed land, old fields, abandoned land)
132 Grassland: managed (golf courses, residential/corporate lawn, parks)
133 Grassland: airports
Upland Forest
141 Upland forest: deciduous (>66% deciduous)
142 Upland forest: mixed deciduous/coniferous
143 Upland forest: coniferous (>66% evergreen)
145 Upland forest: scrub/shrub)
241 Wetland forest: deciduous (>66% deciduous)
242 Wetland forest: mixed deciduous/coniferous
243 Wetland forest: coniferous (>66% coniferous)
245 Wetland scrub/shrub: mixed deciduous/evergreen
160 Barren soil/rock (sand/gravel pits, barren < 25% vegetation)
200 Unconsolidated shore
230 Riverine/lacustrine/palustrine emergent marshes: mixed species
252 Riverine/lacustrine/palustrine open water
Not charted due to absence or less than 1% of total composition.
210 Estuarine Emergent Wetland
251 Marine/Estuarine Open water.
The Highlands study regional 2000 land cover, currently in its draft version, is an update of 1999 and 2000 land use data merged with the 1995 land cover data. The land use updates used spectral merges of 1999/2000 SPOT panchromatic image mosaics (10-meter resolution) and Landsat 7 ETM+ September 23, 1999 imagery. The 1995 land cover was derived primarily from the classification of Landsat thematic mapper satellite imagery dated November 4, 1994 and September 4, 1995. Additionally, ancillary data from a variety of sources were used to aid in the mapping procedures.
The land covered is clipped by the geographic extent of the 99/00 land use updates: in New Jersey by any 3.75 minute quarter quadrangle which overlaps with the New York-New Jersey highlands study area boundary. In New York, the updates are bound by the study area boundary except for Westchester Country.
Currently no metadata document exists for this draft data set, however, listed below are characteristics of the land cover data. The level 3 land cover data are provided by CRSSA as-is and are intended for further copying and dissemination. These data have not yet been accuracy assessed.
Format: Arc Info raster grid (A/I vers. 8.1)
Grid name: nynhjpre00nmcr
Grid cell resolution: 30 x 30 meters
Geo-reference information: projection UTM, Spheroid: GRS 1980; Datun: NAD83; Units: Meters; UTM Zone 18.
Appendix
3-G. STATSGO soil units.
The tables provided below were developed by the New York State Department of Environmental Conservation, Geographic Information Systems Group in 2001 and 2002 using STATSGO map unit digital data (USDA NRCS 1994).
This data set is a digital general soil association map
developed by the National Cooperative Soil Survey and distributed by the
Natural Resources Conservation Service (formerly Soil Conservation Service) of
the U.S. Department of Agriculture. It
consists of a broad based inventory of soils and nonsoil areas that occur in a
repeatable pattern on the landscape and that can be cartographically shown at
the scale mapped. The soil maps for
STATSGO are compiled by generalizing more detailed soil survey maps. Where more detailed soil survey maps are not
available, data on geology, topography, vegetation, and climate are assembled,
together with Land Remote Sensing Satellite (LANDSAT) images. Soils of like areas are studied, and the
probable classification and extent of the soils are determined.
The approximate minimum area delineated is 625 hectares (1,544 acres), which is represented on a 1:250,000-scale map by an area approximately 1 cm by 1 cm (0.4 inch by 0.4 inch). Linear delineations are not less than 0.5 cm (0.2 inch) in width. The number of delineations per 1:250,000 quadrangle typically is 100 to 200, but may range up to 400. Delineations depict the dominant soils making up the landscape. Other dissimilar soils, too small to be delineated, are present within a delineation. (USDA NRCS 1994).
Table 3-G.1. Distribution (acres) of STATSGO soil map units in
the Bearfort, Kanouse, Bellevale, and Schunemunk Mountains Land Type
Association 221 Ae 01 in New Jersey and New York. (USDA NRCS 1994).
|
Map Unit Identification |
Map Unit Name |
Acres |
Percent |
|
NJ002 |
Swartswood-Oquaga-Rock Outcrop |
19,216 |
42.81% |
|
NY156 |
Bernardston-Nassau-Mardin |
10,519 |
23.43% |
|
NY050 |
Arnot-Oquaga-Lordstown |
10,085 |
22.47% |
|
NY157 |
Charlton-Hollis-Chatfield |
1,783 |
3.97% |
|
NJ010 |
Rockaway-Rock Outcrop-Hibernia |
1,150 |
2.56% |
|
NJW |
Water |
603 |
1.34% |
|
NY149 |
Hoosic-Windsor-Limerick |
601 |
1.34% |
|
NY038 |
Swartswood-Oquaga-Rock Outcrop |
586 |
1.31% |
|
NY080 |
Madalin-Rhinebeck-Canadice |
189 |
0.42% |
|
NY136 |
Wellsboro-Wurtsboro-Lackawanna |
107 |
0.24% |
|
NY039 |
Rockaway-Rock Outcrop-Hibernia |
47 |
0.10% |
Table 3-G.2. Distribution (acres) of STATSGO soil map units in the Rockaway Highlands Land Type Association 221 Ae 02 in New Jersey and New York (USDA NRCS 1994).
|
Map Unit
Identification |
Map Unit Name |
Acres |
Percent |
|
NJ10 |
Rockaway-Rock Outcrop-Hibernia |
218,052 |
77.80% |
|
NJ001 |
Hazen-Chenango-Riverhead |
12,207 |
4.36% |
|
NY039 |
Swartswood-Oquaga-Rock Outcrop |
11,536 |
4.12% |
|
NJW |
Water |
6,999 |
2.50% |
|
NJ011 |
Washington-Wassaic-Bartley |
6,036 |
2.15% |
|
NJ009 |
Carlisle-Sloan-Palmyra |
5,648 |
2.02% |
|
NJ012 |
Urban Land-Dunellen-Riverhead |
4,906 |
1.75% |
|
NJ015 |
Parker-Gladstone-Califon |
3,928 |
1.40% |
|
NJ002 |
Swartswood-Oquaga-Rock Outcrop |
3,576 |
1.28% |
|
NY157 |
Charlton-Hollis-Chatfield |
2,233 |
0.80% |
|
NY001 |
Stockbridge-Georgia-Farmington |
1,753 |
0.63% |
|
NJ004 |
Carlisle-Palms-Wallkill |
866 |
0.31% |
|
NY141 |
Palms-Carlisle-Edwards |
731 |
0.26% |
|
NJ005 |
Stockbridge-Georgia-Farmington |
639 |
0.23% |
|
NY173 |
Carlisle-Palms-Wallkill |
589 |
0.21% |
|
NJ017 |
Washington-Annandale-Bartley |
446 |
0.16% |
|
NY149 |
Hoosic-Windsor-Limerick |
111 |
0.04% |
|
NY136 |
Wellsboro-Wurtsboro-Lackawana |
14 |
0.00% |
|
NY171 |
Urban Land-Dunellen-Riverhead |
7 |
0.00% |
Table 3-G.3. Distribution (acres) of STATSGO soil map units in the New Jersey Highlands Valleys Land Type Association 221 Ae 03 in New Jersey and New York. (USDA NRCS 1994).
Map
Unit Identification
|
Map
Unit Name
|
Acres |
Percent |
|
NJ001 |
Hazen-Chenango-Riverhead |
11,753 |
0.20 |
|
NJ010 |
Rockaway-Rock Outcrop-Hibernia |
8,893 |
0.15 |
|
NJ017 |
Washington-Annandale-Bartley |
6,212 |
0.10 |
|
NY156 |
Bernardston-Nassau-Mardin |
5,932 |
0.10 |
|
NJ011 |
Washington-Wassaic-Bartley |
5,493 |
0.09 |
|
NY149 |
Hoosic-Windsor-Limerick |
4,614 |
0.08 |
|
NJ004 |
Carlisle-Palms-Wallkill |
3,643 |
0.06 |
|
NJ015 |
Parker-Gladstone-Califon |
2,675 |
0.05 |
|
NJ005 |
Stockbridge-Georgia-Farmington |
2,624 |
0.04 |
|
NY080 |
Madalin-Rhinebeck-Canadice |
2,018 |
0.03 |
|
NJ012 |
Urban Land-Dunellen-Riverhead |
1,380 |
0.02 |
|
NJ002 |
Swartswoord-Oquaga-Rock Outcrop |
943 |
0.02 |
|
NJ009 |
Carlisle-Sloan-Palmya |
849 |
0.01 |
|
NY001 |
Stockbridge-Geogia-Farmington |
711 |
0.01 |
|
NY173 |
Carlisle-Palms-Wallkill |