• Category
  • Length Range
    85-110 µm
  • Width Range
    17-19 µm
  • Striae in 10 µm
    5-6 at the center, 6-8 at the ends

Identification

Description

Valves are lanceolate, with apices are broadly rounded, but not protracted. The axial area is narrow and straight, widening to form a rounded to sometimes nearly rectangular central area. The raphe is straight and filiform, with external proximal raphe ends dilated slightly and rounded. Distal raphe ends are hook-like. Striae are distinctly lineate and radiate along most of the valve, becoming parallel to convergent at the apices.

Autecology

Though reported to be widespread in freshwater (Foged 1981, Antoniades et al. 2008), this taxon appears to display more of a circumboreal distribution as suggested by Antoniades et al. (2008). In North America, this taxon has been reported from Alaska (Foged 1981, Hein 1990), Michigan (this page), Prince Patrick Island, Ellesmere Island, Ellef Ringnes Island (Antoniades et al. 2008), the Great Lakes (Reavie and Andresen 2020), the Rocky Mountains in Alberta, British Columbia, Montana, the Olympic Range in Washington, Glaciated Plains such as North Dakota, and sub-arctic tundra in Nunavut (Bahls 2021). Reported to occur in lakes, wetlands, streams and rivers (Bahls 2021).

In the Great Lakes National Parks (Edlund et al. 2011, 2012, 2013), it is common (1-10% relative abundance) in sediment core material from lakes in Isle Royale (Ahmik Lake), Sleeping Bear Dunes (Shell Lake), and rare at St. Croix National Scenic Riverway (Lake St. Croix) (Edlund et al. 2009).

Lim et al. (2007) presented a canonical correspondence analysis (CCA) for their assessment of communities in the Canadian Arctic Archipelago in which it is shown centered near the origin indicating a generalist ecology. Michelutti et al. (2003) presented a CCA showing it to prefer rock substrates, tolerate moss substrates, and be intolerant of sediment substrates. Bahls (2021) reported this taxon to occur in cool alkaline waters with low nutrients and conductivity. Jaques et al. (2016) report this taxon to be associated with the coastal fen ecozone of the Hudson Bay lowlands, characterized by high pH, alkalinity, and conductivity, as well as high concentrations of dissolved inorganic carbon and ions.

Several research groups have used this taxon as indicator organism and published regional environmental optima and tolerances including:

Lim et al. (2001): Total Nitrogen (TN) - 0.716 mg/L, Tolerance – 0.209 mg/L for populations of Bathurst Island.

Lim et al. (2007): TN 0.546 mg/L for populations found on Banks Island.

Antoniades et al. (2008): pH – 8.0, tolerance range - 7.7-8.3, Conductivity – 98 µS/cm, tolerance range -55-176 µS/cm, Dissolved Organic Carbon – 6.38 mg/L, tolerance range 3.75-10.85 mg/L for populations from Prince Patrick Island, Ellesmere Island and Ellef Ringnes Island.

Original Description

  • Author
    Kütz. 1844

Citations & Links

Citations

Links

Updates

Dec 16, 2024 - Correction to basionym

The basionym was incorrectly listed as Pinnularia peregrina Ehrenberg. It was corrected to N. vulpina Kützing and the INA and CAS links were also corrected. - S. Spaulding

Nov 09, 2024 - Addition of Autecology

From 2011 until 2024 the autecological information on this taxon page was limited. As of this update, information on ecology, biogeography, and environmental optima have been added. - Lane Allen & Mark Edlund

Cite This Page

Kociolek, P., Allen, L., Edlund, M. (2011). Navicula vulpina. In Diatoms of North America. Retrieved December 16, 2024, from https://diatoms.org/species/46084/navicula_vulpina

Responses

The 15 response plots show an environmental variable (x axis) against the relative abundance (y axis) of Navicula vulpina from all the stream reaches where it was present. Note that the relative abundance scale is the same on each plot. Explanation of each environmental variable and units are as follows:

ELEVATION = stream reach elevation (meters)
STRAHLER = distribution plot of the Strahler Stream Order
SLOPE = stream reach gradient (degrees)
W1_HALL = an index that is a measure of streamside (riparian) human activity that ranges from 0 - 10, with a value of 0 indicating of minimal disturbance to a value of 10 indicating severe disturbance.
PHSTVL = pH measured in a sealed syringe sample (pH units)
log_COND = log concentration of specific conductivity (µS/cm)
log_PTL = log concentration of total phosphorus (µg/L)
log_NO3 = log concentration of nitrate (µeq/L)
log_DOC = log concentration of dissolved organic carbon (mg/L)
log_SIO2 = log concentration of silicon (mg/L)
log_NA = log concentration of sodium (µeq/L)
log_HCO3 = log concentration of the bicarbonate ion (µeq/L)
EMBED = percent of the stream substrate that is embedded by sand and fine sediment
log_TURBIDITY = log of turbidity, a measure of cloudiness of water, in nephelometric turbidity units (NTU).
DISTOT = an index of total human disturbance in the watershed that ranges from 1 - 100, with a value of 0 indicating of minimal disturbance to a value of 100 indicating severe disturbance.

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