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A3230 Acer platanoides - Ailanthus altissima - Pinus spp. Exotic Ruderal Forest Alliance
Type Concept Sentence: These semi-natural forests are dominated by naturalized Acer platanoides, Ailanthus altissima, Pinus thunbergii, Pinus nigra, or Paulownia tomentosa in the eastern United States.
Common (Translated Scientific) Name: Norway Maple - Tree-of-Heaven - Pine species Exotic Ruderal Forest Alliance
Colloquial Name: Eastern Exotic Ruderal Forest
Hierarchy Level: Alliance
Type Concept: This alliance includes semi-natural forests dominated by naturalized Acer platanoides, Ailanthus altissima, Paulownia tomentosa, Pinus nigra, or Pinus thunbergii. These are all exotic tree species that have locally established in the region. Pinus thunbergii stands occur in the northeastern coastal region and likely beyond, on well-drained to xeric sandy soils, usually on sand dunes or near-coastal glacial tills. Stands are of variable canopy height and closure and dominated by Pinus thunbergii or Pinus nigra. Ailanthus altissima is a native of eastern Asia. This forest occurs mostly in disturbed areas, along roadsides, urban abandoned lands, and on limestone clifftops. In some parts of the range, this forest is associated with calcareous soils. Acer platanoides stands often occur to the exclusion of virtually all other canopy species. Most documented stands are at low elevations, on flat or rolling topography both above and below the glacial boundary. In some stands, native trees, including Fraxinus americana and Acer saccharum (the latter especially susceptible to exclusion by Acer platanoides), may be present in very limited amounts. Other stands may have non-native associates, including Pinus nigra, Pinus sylvestris, or Robinia pseudoacacia. The deep shade cast by Acer platanoides limits understory growth, aside from regeneration of Acer platanoides, or incursions by non-native shrubs such as Rosa multiflora, Berberis vulgaris, Lonicera japonica, or Lonicera morrowii. Native herbs are few, especially compared to more natural deciduous forests in similar settings. A few native or exotic herbaceous species or vines may occupy the ground layer, such as Alliaria petiolata, Eurybia divaricata, Toxicodendron radicans, and Vinca minor. Paulownia tomentosa, a native of Asia, has become naturalized in portions of the eastern United States, where it occurs as small, scattered populations along roadsides, in disturbed woodlots, and in streamside forests.
Diagnostic Characteristics: Forests dominated by Acer platanoides, Ailanthus altissima, Paulownia tomentosa, Pinus nigra, or Pinus thunbergii, that singly or together have >80% canopy cover.
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: This alliance contains a somewhat heterogeneous set of exotic tree species that dominate or have invaded a variety of disturbed sites. Further review may show that a suite of associated species that differentiate different site types can be used to refine or split the alliance. Currently the mix of species includes Acer platanoides, Ailanthus altissima, Paulownia tomentosa, Pinus nigra, or Pinus thunbergii, which have come to dominate a site to the point that the pre-invasion forest type cannot be distinguished. Where forests have been invaded, but where sufficient native trees and other flora still exist to determine the pre-invasion forest type, they are classified as degraded examples of those pre-invasion types.
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: Stands are open to closed, and range from pure conifer to pure hardwood.
Floristics: These semi-natural forests are dominated by naturalized Acer platanoides, Ailanthus altissima, Paulownia tomentosa, Pinus nigra, or Pinus thunbergii. These are all exotic tree species that have locally established in the region. Pinus thunbergii stands occur in the northeastern coastal region and likely beyond. Stands are of variable canopy height and closure and dominated by Pinus thunbergii or Pinus nigra. A frequent canopy associate can be Pinus rigida. The shrub layer is not well-developed, and the herbaceous layer is of variable composition. Toxicodendron radicans is common in all strata of this community (Sneddon and Lundgren 2001). Ailanthus altissima is a native of eastern Asia. This forest occurs mostly in disturbed areas, along roadsides, urban abandoned lands, and on limestone clifftops. In some parts of the range, this forest is associated with calcareous soils. Acer platanoides stands often occur to the exclusion of virtually all other canopy species. Most documented stands are at low elevations, on flat or rolling topography both above and below the glacial boundary. Acer platanoides is the overwhelmingly dominant tree, typically forming a closed or nearly closed canopy. In some stands native trees, including Fraxinus americana and Acer saccharum (the latter especially susceptible to exclusion by Acer platanoides), may be present in very limited amounts. Other stands may have non-native associates, including Pinus nigra, Pinus sylvestris, or Robinia pseudoacacia. The deep shade cast by Acer platanoides limits understory growth, aside from regeneration of Acer platanoides, or incursions by non-native shrubs such as Rosa multiflora, Berberis vulgaris, Lonicera japonica, or Lonicera morrowii. Native herbs are few, especially compared to more natural deciduous forests in similar settings. A few native or exotic herbaceous species or vines may occupy the ground layer, such as Alliaria petiolata, Eurybia divaricata (= Aster divaricatus), Toxicodendron radicans, and Vinca minor (Patterson 1976). Paulownia tomentosa forests are found on disturbed, usually steep and rocky areas. This species is native to eastern Asia, where it is a minor component of deciduous mesophytic forests. It has become naturalized in portions of the eastern United States, where it occurs as small, scattered populations along roadsides, in disturbed woodlots, and in streamside forests (Williams 1993).
Dynamics: The long-term persistence of these stands is not clear. They are not likely to become strongly invasive, since they require large-scale, substrate-scarifying disturbance for optimal establishment and maintenance (Patterson 1976, Williams 1993, Sneddon and Lundgren 2001).
Environmental Description: These forests occur mostly in disturbed areas, along roadsides, on well-drained to xeric sandy soils, including sand dunes or near-coastal glacial tills, steep rocky sites, urban abandoned lands, and calcareous sites (Patterson 1976, Williams 1993, Sneddon and Lundgren 2001).
Geographic Range: The alliance is localized but widespread, occurring in locally disturbed areas throughout the Midwest, Northeast and Central United States.
Nations: CA?,US
States/Provinces: AR, CT, DE, KY, MA, NC, NJ, NY, ON?, PA, RI, TN, VA, WV
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.899354
Confidence Level: Low
Confidence Level Comments: No Data Available
Grank: GNA
Greasons: No Data Available
Type | Name | Database Code | Classification Code |
---|---|---|---|
Class | 1 Forest & Woodland Class | C01 | 1 |
Subclass | 1.B Temperate & Boreal Forest & Woodland Subclass | S15 | 1.B |
Formation | 1.B.2 Cool Temperate Forest & Woodland Formation | F008 | 1.B.2 |
Division | 1.B.2.Na Eastern North American Forest & Woodland Division | D008 | 1.B.2.Na |
Macrogroup | 1.B.2.Na.90 Black Locust - Tuliptree - Norway Maple Ruderal Forest Macrogroup | M013 | 1.B.2.Na.90 |
Group | 1.B.2.Na.90.b Norway Maple - Black Locust - Scotch Pine Exotic Ruderal Forest Group | G032 | 1.B.2.Na.90.b |
Alliance | A3230 Norway Maple - Tree-of-Heaven - Pine species Exotic Ruderal Forest Alliance | A3230 | 1.B.2.Na.90.b |
Association | CEGL003687 Princess-tree Ruderal Woodland | CEGL003687 | 1.B.2.Na.90.b |
Association | CEGL006012 Japanese Black Pine - (Austrian Pine) Ruderal Forest | CEGL006012 | 1.B.2.Na.90.b |
Association | CEGL006407 Norway Maple Ruderal Forest | CEGL006407 | 1.B.2.Na.90.b |
Association | CEGL007191 Tree-of-Heaven Ruderal Forest | CEGL007191 | 1.B.2.Na.90.b |
Concept Lineage: parts of A.216, A.221, A.609, A3016
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: No Data Available
- Faber-Langendoen, D., J. Drake, M. Hall, G. Kittel, S. Menard, C. Nordman, M. Pyne, M. Reid, M. Russo, K. Schulz, L. Sneddon, K. Snow, and J. Teague. 2013-2019b. Screening alliances for induction into the U.S. National Vegetation Classification: Part 1 - Alliance concept review. NatureServe, Arlington, VA.
- Patterson, D. T. 1976. The history and distribution of five exotic weeds in North Carolina (Ailanthus altissima, Lonicera japonica, Polygonum cuspidatum, Pueraria lobata, Rosa multiflora). Castanea 41:177-180.
- Sneddon, L., and J. Lundgren. 2001. Vegetation classification of Fire Island National Seashore and William Floyd Estate. Final Draft. TNC/ABI Vegetation Mapping Program. 87 pp.
- Williams, C. E. 1993. Age structure and importance of naturalized Paulownia tomentosa in a central Virginia streamside forest. Castanea 58:243-249.