Valves are linear to linear-lanceolate, with parallel margins. The distal valve tapers abruptly to form slightly protracted to rounded apices. Fibulae are distinct, numbering 11-13 in 10 µm. Striae are parallel and finely punctate.
This taxon has been reported with light micrographs from northern Québec and Labrador (Fallu et al. 2000), the Canadian Arctic Archipelago (Antoniades et al. 2008), the Atlantic Coastal Plain (Siver and Hamilton 2011), and Western North America (Bahls 2023).
In the Great Lakes National Parks (Edlund et al. 2009, 2011, 2012, 2013), this taxon is common (5-25% abundance) in sediment core material from Apostle Islands (Outer Lake) and uncommon (1-5% abundance) to rare (0.1-1% abundance) at Isle Royale (Richie and Ahmik lakes), Pictured Rocks (Grand Sable Lake), Voyageurs (Mukooda, Ek, Brown and Cruiser lakes), Sleeping Bear Dunes (Florence Lake), and St. Croix Scenic Riverway (Lake St. Croix).
This taxon is known to occur in ponds, lakes and streams with cool, weakly alkaline water of moderate conductivity and nutrient content (Bahls 2023).
Many research groups consider this taxon an indicator organism and published regional environmental optima and tolerances including:
Fallu et al. (2000): Dissolved Organic Carbon - 6.39 +/- 1.52 mg/L for “form 1 QUEBEC”, 5.05 +/- 1.53 mg/L for “form 2 QUEBEC”, Color - 14 +/- 3.0 Pt units, Alkalinity - 37 +/- 2.3 µeq/L for populations from northern Québec and Labrador.
Antoniades et al. (2008): pH - 7.8, Tolerance Range - 7.1-8.5, Conductivity - 135 µS/cm, Tolerance Range - 47-386 µS/cm, Dissolved Organic Carbon - 3.19 mg/L, Tolerance Range - 1.50-6.81 µS/cm for populations from the Canadian Arctic Archipelago.
Siver and Hamilton (2011): Abundance Weighted Mean (AWM) pH - 6.4 +/- 0.7, AWM total phosphorus (TP) - 10.9 +/- 3.2 µg/L.
Bahls (2023): Conductivity - 573 µS/cm, pH - 7.5, Temperature - 14.6°C, Total Nitrogen - 1.25 mg/L, TP - 149 µg/L.
From 2011 until 2026, autecological information on this taxon page was limited. As of this update, information on ecology, biogeography, and environmental optima have been added. - Lane Allen and Mark Edlund
Kociolek, P., Edlund, M., Allen, L. (2011). Nitzschia perminuta. In Diatoms of North America. Retrieved March 23, 2026, from https://diatoms.org/species/46776/nitzschia_perminuta
The 15 response plots show an environmental variable (x axis) against the relative abundance (y axis) of Nitzschia perminuta 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.