• Category
  • Length Range
    65-130 µm
  • Width Range
    18-28 µm
  • Striae in 10 µm
    7-9

Identification

Description

Valves are elliptic-lanceolate with broadly rounded and slightly protracted ends. Axial area is narrow, linear, about twice the width of the raphe. Central area is broad and transversely rectangular with rounded corners and irregular borders formed by shortened striae of various lengths. Raphe is lateral, becoming filiform near the proximal ends, which are triangular in shape and deflected slightly toward the secondary side. Striae are mostly radiate, becoming parallel and finally somewhat convergent near the valve ends. Areolae are fine, 26-28 in 10 µm. Voigt discontinuities are clearly evident on the secondary side.

Autecology

This taxon has been recorded in the benthos of streams and lakes, primarily in the Pacific Northwest. It prefers cool and somewhat alkaline waters with low conductivity and low to moderate concentrations of nutrients. Common associates in the Northwest include Diploneis ovalis, Nitzschia innominata, Planothidium peragalli, Planothidium daui, Cavinula cocconeiformis, Geissleria schoenfeldii, Achnanthes oblongella, Planothidium rostratum, Planothidium lanceolatoides, and Achnanthidium rivulare (Bahls 2011).

Originally described based on populations from Crater Lake, Emerald Pool, and Diamond Lake with a total of 30 collections reported from Washington state (Sovereign 1958). Reported to be widespread in the Pacific Northwest (Sovereign 1958, Patrick and Reimer 1966). In North America, this taxon has been reported from Washingthon, Oregon (Sovereign 1958), mountain streams and lakes in the Rockies, the Coast and Cascade ranges and the Sierras (Bahls 2021) and Alaska (Foged 1981).

In the Great Lakes National Parks (Edlund et al. 2011, 2012, 2013), it is rare except (>1% relative abundance) in sediment core material from Shell Lake in Sleeping Bear Dunes National Lakeshore.

Originally reported from slightly alkaline waters (Sovereign 1958) Foged (1981) stated “Oligohalobe (indifferent). pH: indifferent” regarding populations from Alaska. Bahls (2021) reported this taxon to prefer cold alkaline waters with moderate nutrients and conductivity. This is also supported by the report by Clark and Rushforth (1977) regarding the abundance of this diatom in their study of the headwaters of Henry’s Fork in Idaho.

Both Clark and Rushforth (1977) and Bahls (2021) report this taxon to be highly variable in morphology, with Bahls specifying that lacustrine populations are typically larger than those found in lotic systems.

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

Sovereign (1958): pH tolerance range 6.5-9.0 for populations from the Pacific Northwest.

Bahls (2021): pH – 8.0, Conductivity – 213 µS/cm, Temperature – 12.4 °C , Total Nitrogen – 0.590 mg/L, Total Phosphorus – 57 µg/L for populations from the western US.

Our  Lake
Credit: Loren Bahls
Our Lake, Teton County, Montana: home of Navicula aurora
Navicula Aurora Chem 001
Credit: Montana Diatom Database
Abundance-weighted mean values for selected water quality variables measured concurrently with the collection of samples containing Navicula aurora.

Original Description

Valvae elliptico vel lineari-lanceolatae apicibus obtusis late rotundatis, subprotractis, 59-118 µ longae, 15-26 µ latae; raphe directa fissuris terminalibus longis in eandem partem flexis, area axialis distincta, linearis, modice lata, area centralis lata, transapicaliter elliptica; striae transapicales 6.3 ad 7.5 in 10 µ, radiantes, prope apices ad lineam mediam perpendiculares, distincte lineolatae.

  • Author
    Sovereign 1958
  • Length Range
    59-118 µm
  • Width
    15-26 µm
  • Striae in 10µm
    6.3-7.5

Original Images

N Aurora Original Images
N Aurora Original Description

Citations & Links

Citations

Links

  • Index Nominum Algarum
  • North American Diatom Ecological Database
    NADED ID: 46167

Updates

Oct 29, 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

Bahls, L., Allen, L., Edlund, M. (2011). Navicula aurora. In Diatoms of North America. Retrieved December 03, 2024, from https://diatoms.org/species/navicula_aurora

Responses

The 15 response plots show an environmental variable (x axis) against the relative abundance (y axis) of Navicula aurora 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.