Valves are large and linear to linear-elliptic, with cuneate apices. The valve face is flat. Valve margins are nearly parallel to slightly convex. Multiple longitudinal lines(3-5) are present along the valve margin. The axial area is straight to slightly expanded. In the largest specimens, the axial area may bear irregular markings on both sides of the raphe, while the axial area tends to be hyaline in small to medium sized specimens. The raphe is mostly oblique, becoming thread-like near the terminal end. Proximal raphe ends are small and strongly hooked in opposite directions. Distal raphe ends form lacinia, although this feature is difficult to resolve in LM. Internally, valves bear a rectelevatum. Helictoglossae are small, but can be resolved in focal deep planes.
The striae are slightly oblique across most of the valve face, but the angle of the striae differs bilaterally at the apices, with striae becoming parallel on opposite sides of the raphe at each apex. The central area is elliptic and slightly elongate along the transapical axis. Voigt’s discontinuities, when present, are subtle. Areolae are relatively small and round near the axial area, becoming large and transapically elongate near the valve margin.
Ehrenberg's type material contained specimens up to 167 µm long and 42 µm wide (Lefebvre and Hamilton 2015). The smallest specimen presented here is smaller than the minimum length reported elsewhere (Siver and Hamilton 2011, Lefebvre and Hamilton 2015). The maximum length observed in this population close to the maximum length reported in modern populations (Lefebvre and Hamilton 2015).
Externally, areolae are open. Internally, areolae are occluded by a hymen (Siver and Hamilton 2011). Renilimbia are located near areolae across the valve face (Lefebvre and Hamilton 2015). The valve walls are chambered both apically and transapically (Lefebvre and Hamilton 2015), similar to N. rudimentarum, N. ampliatum, N. gracile, N. hitchcockii, and N. tumescens (Hamilton et al. 2004).
Although the clarification of morphological features has helped reduce errors in identification of large Neidium, note that older literature may be misleading. For example, specimens presented in some sources (Krammer and Lange-Bertalot 1986), differ from more recent species boundaries (Lefebvre and Hamilton 2015).
This taxon has been reported from lake, pond, and wetland habitats, from sites in Ontario and New York (Lefebvre and Hamilton 2015), England (Patrick and Reimer 1966). The specimens illustrated here were collected from a marsh near Brainard Lake and Lake Clayton in the Indian Peaks Wilderness of Colorado.
Seven syntypes were submitted by Ehrenberg, six from the US and one from Mexico, however a holotype was not designated. In 2015, Lefebvre and Hamilton lectotypified the population from Andower, Massachusetts. Broadly distributed in boreal habitats. This taxon has been reported with light micrographs from the northeastern US (Camburn and Charles 2000), North Carolina, New Jersey (Siver and Hamilton 2011), the Rocky Mountains, Cascade Mountains, and Olympic Mountains (Bahls, 2023). This taxon is known to occur in ponds, lakes, tarns, springs, and wetlands.
In the Great Lakes National Parks (Edlund et al., 2011, 2012, 2013) this taxon occurs as a trace component of the sediment core community at Voyageurs (Shoepack and Brown lakes).
This taxon is perhaps the most common of the large Neidium species in North America, though like many large taxa, it typically occurs in low abundances relative in the community. Large taxa are typically underestimated using traditional counting techniques and larger cells may have greater importance in communities (Snoeijs et al. 2002).
Bahls (2023) reports this taxon to prefer cool, circumneutral waters with low conductivity.
Several research groups have used this taxon as an indicator organism and published regional environmental optima and tolerances including:
Camburn and Charles (2000): pH - 5.15 +/- 0.70, Acid Neutralizing Capacity – 11 +/- 42 µeq/L, Total Aluminum – 126 +/- 183 µg/L, Dissolved Organic Carbon – 162 +/- 168 µmol/L, Total Phosphorus (TP) – 8.87 +/- 9.53 µg/L for populations from lakes in northeastern US.
Siver et al. (2005): pH - 5.6 +/- 0.9, TP – 9 +/- 2 µg/L
Siver and Hamilton (2011): pH – 5.4 +/- 1.0, TP – 12 +/- 10 µg/L
From 2023 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
Araujo, C., Allen, L., Edlund, M. (2022). Neidium amphigomphus. In Diatoms of North America. Retrieved April 28, 2025, from https://diatoms.org/species/220322/neidium-amphigomphus
The 15 response plots show an environmental variable (x axis) against the relative abundance (y axis) of Neidium amphigomphus 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.