Valves are linear-elliptic. The raphe valve has a narrow axial area and transversely rectangular central area that reaches both valve margins. The rapheless valve has a lanceolate axial area and no distinct central area, though the two middle striae may be slightly more distant from each other than less central striae. The raphe is straight, with slightly expanded terminal and central ends, without terminal fissures. Internally (SEM), the central raphe ends curve toward opposite sides. Striae are almost parallel in the valve center, but become strongly radiate approaching the poles of both valves, biseriate, 12-16 in 10 µm. A single row of areolae exists on the valve mantle, with each areola opposed to a biseriate stria. The external and internal openings of the areolae are circular or somewhat angular, isodiametric.
This taxon has been widely reported from boreal habitats. Populations reported with light micrographs in North America are from British Columbia (Cumming et al. 1995), St. Lawrence River (Reavie and Smol 1998), Northern Alberta and the Northwestern Territiories (Moser et al. 2004), the Great Lakes (Reavie 2020), the Rocky Mountains, the Cascades Mountains, Coast Ranges, and Sierra Nevada Mountains (Bahls 2021). This taxon is known to occur in mountain streams, lakes, and wetlands (Bahls 2021).
In the Great Lakes National Parks (Edlund et al. 2009, 2011, 2012, 2013), this taxon is widely distributed but rare at Voyageurs (Cruiser), Isle Royale (Ahmik, Harvey), Sleeping Bear Dunes (Manitou), Pictured Rocks (Grand Sable) and the St. Croix National Scenic Riverway (Lake St. Croix).
Reported to prefer cool alkaline waters with low levels of nutrients and conductivity (Bahls 2021). This taxon is reported to be a strong indicator of moderately stressed ecosystems (Reavie 2020).
Many research groups have used this taxon as an indicator organism and published regional environmental optima and tolerances including:
Wilson et al. (1994): Optimum Salinity – 0.13 g/L, Range - 0.03 – 0.53 g/L from the Interior Plateau of British Columbia.
Cumming et al. (1995): Optimum Total Phosphorus (TP) – 9.2 µg/L, TP range – 4.3 - 20.0 µg/L, optimum salinity 0.13 g/L, range – 0.03 – 0.53 g/L from lakes in British Columbia.
Reavie and Smol (2001): TP – 18 µg/L, pH – 8.15, Total Nitrogen (TN) – 0.494, Maximum Depth – 18.4 m, Chlorophyll a – 1.78 mg/L from alkaline lakes in outheastern Ontario.
Ruhland et al. (2003): Dissolved Inorganic Carbon - 22.1 mg/L, TN – 0.878 mg/L, Dissolved Organic Carbon – 21.0 mg/L, Depth – 4.4 m, SiO2 – 0.9 mg/L from lakes in the Central Canadian Arctic.
Moser et al. (2004): pH – 8.2, Conductivity – 235 µS/cm from boreal forest lakes in Northern Alberta and the Northwest Territories.
Reavie (2020): Report the optimum TP to be between 10 and 30 µg/l, and optimum Cl to be below 10 µg/l from the Great Lakes.
Bahls (2021): pH – 7.6, Conductivity – 140 µS/cm, Temperature – 12.8 °C, TN – 0.250 mg/L, TP – 84 µg/L for populations from the Rocky Mountains, the Cascades, Coast Ranges, and Sierras.
A. valvis prorsus ovalibus finibus rotundatis, 0,01—0,012 mm longis, 0,0055 mm latis; striis paene parallelis, ad fines subradiantibus, duobus mediis utriusque valvae perspicue distinctis, ab interiore parte ad exteriorem subappropin-quantibus, interdum una stria tenuissima in valva inferiore inter strias medias magis distantes intercalata, striis validis, 13—14 intra 0,01 mm
From 2010 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
Potapova, M., Allen, L., Edlund, M. (2010). Platessa conspicua. In Diatoms of North America. Retrieved January 17, 2025, from https://diatoms.org/species/45105/platessa_conspicua
The 15 response plots show an environmental variable (x axis) against the relative abundance (y axis) of Platessa conspicua 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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