Print Report
CEGL001990 Sparganium angustifolium Aquatic Vegetation
Type Concept Sentence: No Data Available
Common (Translated Scientific) Name: Narrowleaf Bur-reed Aquatic Vegetation
Colloquial Name: No Data Available
Hierarchy Level: Association
Type Concept: This aquatic association has been found in California, Oregon, Washington and Colorado, but likely occurs in many parts of montane, subalpine, alpine and boreal North America as this circumboreal species is reported from the western and northeastern U.S., Great Lakes region, across Canada and Alaska and likely is has a much wider distribution. This hydromorphic-rooted vegetation occurs in shallow water to 1 m deep. Stands occur in saturated or inundated sites such as swales and wet meadows and marshes, shallow ponds and near the shoreline of deeper ponds and lakes. Sites are generally permanently flooded but can be semipermanently flooded areas that lack standing water towards the end of the growing season. If the stand has dried, then bare soil and small rocks are exposed. The ponds are often located in mountain parks or meadows and are the result of stream oxbows or glacial basins in broad valleys. Soils are typically very poorly drained muck or peat and can contain embedded cobbles or rocks. Stands grow equally well on either gravelly or muddy bottoms. Salinity of water varies with the different parent materials. Diagnostic of this aquatic community is the strong dominance of Sparganium angustifolium. Vegetation consists of moderately dense mats of the hydromorphic-rooted plant Sparganium angustifolium. These vegetation mats are rarely over 0.6 m thick and may be much less depending on the depth of the pond. Stunted individuals may be less than 10 cm tall. Associated species with low cover include Alisma triviale, Beckmannia syzigachne, Carex utriculata, Cicuta douglasii, Eleocharis palustris, Equisetum fluviatile, Galium trifidum, Glyceria borealis, Hippuris vulgaris, Lemna minor, Sium suave, or Typha spp. Diagnostic of this aquatic association is the dominance of Sparganium angustifolium.
Diagnostic Characteristics: No Data Available
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: This association is defined as a PNV vegetation type. If it were renamed as a dominance type, the species would include Sparganium americanum and Sparganium natans.
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: No Data Available
Floristics: This aquatic association is characterized by moderately dense to dense mats of the hydromorphic-rooted plant Sparganium angustifolium. These vegetation mats are rarely over 0.6 m thick and may be much less depending on the depth of the pond. Stunted individuals may be less than 10 cm tall. Associated species with low cover include Alisma triviale, Beckmannia syzigachne, Carex utriculata, Cicuta douglasii, Eleocharis palustris, Equisetum fluviatile, Galium trifidum, Glyceria borealis, Hippuris vulgaris, Lemna minor, Sium suave, or Typha spp. (Kovalchik 1993, Hall and Hansen 1997). Vegetation on adjacent mudflats and shorelines is dominated by shrub or herbaceous wetland plants such as Eleocharis acicularis, Ranunculus trichophyllus var. trichophyllus, Callitriche palustris, Schoenoplectus acutus (= Scirpus acutus), Typha latifolia, or species of Carex, Juncus or Salix.
Dynamics: No Data Available
Environmental Description: This aquatic association has been found in California, Oregon, Washington and Colorado, but likely occurs in many parts of montane, subalpine, alpine and boreal North America as this circumboreal species is reported from the western and northeastern U.S., Great Lakes region, across Canada and Alaska and likely is has a much wider distribution. Elevations range from 760 to 3700 m (2500-12,130 feet). This hydromorphic-rooted vegetation occurs in shallow water to 1 m deep. Stands occur in saturated or inundated sites such as swales and wet meadows and marshes, shallow ponds and near the shoreline of deeper ponds and lakes. Sites are generally permanently flooded but can be semipermanently flooded areas that lack standing water towards the end of the growing season. If the stand has dried, then bare soil and small rocks are exposed. The ponds are often located in mountain parks or meadows and are the result of stream oxbows or glacial basins in broad valleys. Soils are typically very poorly drained muck or peat and can contain embedded cobbles or rocks. Stands grow equally well on either gravelly or muddy bottoms. One soil in Colorado was classified as a Cryosaprist (Komarkova 1986). In Oregon, soils are Limnic, Hemic, Sapric, or Fibric Histisols with organic layer 35 cm or more deep (Kovalchik 1993). In Idaho, soils classify to Mollisols, Histosols or Entisols (Hall and Hansen 1997). Salinity of water varies with the different parent materials.
Geographic Range: It is likely that this nearly monospecific association occurs in many parts of montane, subalpine and boreal North America; presently it has been identified from California, Washington, Oregon, Idaho and Colorado.
Nations: US
States/Provinces: CA, CO, ID, OR, WA
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.689289
Confidence Level: High
Confidence Level Comments: No Data Available
Grank: G4
Greasons: No Data Available
Type | Name | Database Code | Classification Code |
---|---|---|---|
Class | 5 Aquatic Vegetation Class | C05 | 5 |
Subclass | 5.B Freshwater Aquatic Vegetation Subclass | S13 | 5.B |
Formation | 5.B.2 Temperate to Polar Freshwater Aquatic Vegetation Formation | F057 | 5.B.2 |
Division | 5.B.2.Na North American Freshwater Aquatic Vegetation Division | D049 | 5.B.2.Na |
Macrogroup | 5.B.2.Na.2 Rocky Mountain Pond-lily - Pacific Mosquito Fern - Western Waterweed Western North American Freshwater Aquatic Vegetation Macrogroup | M109 | 5.B.2.Na.2 |
Group | 5.B.2.Na.2.a Pond-lily species - Pondweed species - Duckweed species Freshwater Aquatic Vegetation Group | G544 | 5.B.2.Na.2.a |
Alliance | A3893 Common Mare''s-tail - Widgeonweed species - Bur-reed species Aquatic Vegetation Alliance | A3893 | 5.B.2.Na.2.a |
Association | CEGL001990 Narrowleaf Bur-reed Aquatic Vegetation | CEGL001990 | 5.B.2.Na.2.a |
Concept Lineage: No Data Available
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: = Sparganium angustifolium - Ranunculus trichophyllus Community (Cooper 1986a)
= Sparganium angustifolium (McCain and Christy 2005) [11 plots]
= Sparganium angustifolium (Sawyer et al. 2009) [52.010.01]
= Sparganium angustifolium (S. emersum) Association (Crowe et al. 2004)
= Sparganium angustifolium Aquatic Community (Robbins 1918) [Sparganium angustifolium dominates second seral stage of glacial lake succession.]
= Sparganium angustifolium Association (Fuller 1930)
= Sparganium angustifolium Association (Christy 2004)
= Sparganium angustifolium Habitat Type/Association (Komarkova 1986)
= Sparganium angustifolium Herbaceous Vegetation [Provisional] (Keeler-Wolf et al. 2012)
= Sparganium emersum Community Type (Hall and Hansen 1997)
= Sparganium emersum association (Stumpf et al. 2017)
= Sparganium emersum community type (Kunze 1994) [(pp.50, 59)]
< Sparganium spp. Association (Kovalchik 1993) [(p.185) either Sparganium emersum and/or Sparganium minium dominated the vegetation layer.]
< Bur-reed Series (Sawyer and Keeler-Wolf 1995) [from sea level to 3700 m elevation; includes several species of Sparganium.]
>< Montane and Subalpine Lakes (Ramaley 1919a) [Sparganium angustifolium replaces Eleocharis lacustris.]
= Simplestem Bur-reed Herbaceous Vegetation (Sparganium angustifolium) (Christy et al. 1998) [(p.138)]
= Sparganium angustifolium (McCain and Christy 2005) [11 plots]
= Sparganium angustifolium (Sawyer et al. 2009) [52.010.01]
= Sparganium angustifolium (S. emersum) Association (Crowe et al. 2004)
= Sparganium angustifolium Aquatic Community (Robbins 1918) [Sparganium angustifolium dominates second seral stage of glacial lake succession.]
= Sparganium angustifolium Association (Fuller 1930)
= Sparganium angustifolium Association (Christy 2004)
= Sparganium angustifolium Habitat Type/Association (Komarkova 1986)
= Sparganium angustifolium Herbaceous Vegetation [Provisional] (Keeler-Wolf et al. 2012)
= Sparganium emersum Community Type (Hall and Hansen 1997)
= Sparganium emersum association (Stumpf et al. 2017)
= Sparganium emersum community type (Kunze 1994) [(pp.50, 59)]
< Sparganium spp. Association (Kovalchik 1993) [(p.185) either Sparganium emersum and/or Sparganium minium dominated the vegetation layer.]
< Bur-reed Series (Sawyer and Keeler-Wolf 1995) [from sea level to 3700 m elevation; includes several species of Sparganium.]
>< Montane and Subalpine Lakes (Ramaley 1919a) [Sparganium angustifolium replaces Eleocharis lacustris.]
= Simplestem Bur-reed Herbaceous Vegetation (Sparganium angustifolium) (Christy et al. 1998) [(p.138)]
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