Northern Prairie Wildlife Research Center
Colloquial names for sago in the United States include duck grass, duck moss, eelgrass, fennel pondweed, foxtail, Indian grass, old-fashioned bay grass, pondgrass, potato moss, and wild celery (McAtee 1939). In Europe, sago has been called poker and pochard grass (McAtee 1917) and, in Australia, string weed (Fletcher et al. 1985).
In North America, sago is placed with P. filiformis and P. vaginatus in the subgenus Coleogeton, in which all leaves are linear or setaceous, nonfloating, and divided their full length by crosspartitions (Fernald 1950). Harrison (1949) claims members of this subgenus are, unlike others, water pollinated. The three coleogetonous species have also been shown to form a distinct subgroup based on the chemistry of the waters they inhabit (Pip 1987). In the field, sago can be differentiated from the two other coleogetonous species by the presence of usually sharp-tipped or gradually pointed leaves and leaf sheaths that are rather narrow but free at the tips.
Sago has an average of 2n = 78 (70-87) chromosomes (Kalkman and Van Wijk 1984). Analyses of isoenzymes indicated that the species is genetically very heterogeneous (Hettiarachchi and Triest 1986; Van Wijk et al. 1988). Sago hybridizes with Potamogeton filiformis (P. x suecicus Richt.) and P. vaginatus (Hagstrom 1916; Dandy and Taylor 1946; Harrison 1949). Meriaux (1978) and Van Wijk (1988) reviewed the work of many European taxonomists who named many varieties or "proles" of sago (dichotomus Wallr., drupaceus Koch, flabellatus Crep., interceptus Asch., protensus Wallr., setaceus Mey., scoparius Wallr., vulgaris Cham. and Schl., and zosteraceus Fries). Both questioned whether these are simple morphs or truly have value as indicators of specific biotopes or habitat types. Luther (1951, cited in Van Wijk 1983) also concluded that the different types of sago were habitat modifications. The varieties interruptus Asch., pectinatus, and scoparius have been maintained in a recent European flora, although their taxonomic validity is said to be unclear (Casper and Krausch 1980, cited in Van Wijk 1988). Van Wijk (1983) found different morphological and ecological characteristics of annual and perennial P. pectinatus in the field and in cultured plants and recommended that the existence of these ecotypes be considered when studying the taxon. Wiegleb (1978) associated the variety scoparius with HCO3-poor waters and the variety interruptus with sites polluted with sewage. Recent work has shown that genetic differentiation does occur in sago and must be considered along with morphological characters if the taxonomy of the species is to be clarified (Van Wijk et al. 1988).
Meriaux (1978) reviewed the work of devotees of the Zurich-Montpellier school of phytosociology (Braun-Blanquet 1932) who placed sago in various orders, alliances, and associations with other species in this elaborate phytosociological classification system. Sago was also recognized as a character or dominant species in several European and Asian associations by Hejny and Husak (1978). Sago is the most prominent plant in the Potamogeton facies of several estuarine plant communities in Europe (Kornas et al. 1960) and a faithful taxon in the class Potamea (den Hartog and Segal 1964) in some wetlands in India (Zutshi 1975). Sago also is a member of several Chara-, Ruppia-, and Zannichellia- dominated communities in the Baltic, Mediterranean, and Eurosiberian regions (Lindner 1978; Verhoeven 1980a; Van Vierssen 1982a).
Sago can be considered a pioneering species, because it quickly inhabits newly flooded areas (Nelson 1954) and invades shallow waters with relatively strong wave action (Ozimek and Kowalczewski 1984) or those that are polluted (Haslam 1978). Sago is one of the first species to colonize areas reclaimed from the sea (Wolseley 1986). den Hartog (1963) and Van Vierssen (1982a) considered sago a survivor species that often showed mass development in areas where the environment became temporarily unsuitable for other species. Davis and Brinson (1980) placed sago in a group of plants tolerant of, and able to maintain dominance in, altered ecosystems.
Sago is found in submerged, floating-leaved, and emergent communities. Best plant development occurs in submerged communities, and the poorest in emergent communities where sago plants tend to be short in stature (Van der Valk and Bliss 1971). In general, most other growth forms of hydrophytes, except similar types such as charids, valisnerids, and ceratophyllids, negatively influence the environment for parvopotamids, usually because of competition for light (Hogeweg and Brenkert 1969).
Most submersed macrophytes are sensitive to frost damage (Lohammar 1938). This, combined with the rapid decomposition of plants in water, causes sago to usually behave as an annual in shallow waters in temperate climates, with buried turions the only vegetative structure to survive winter (Lapirov and Petukhova 1985). However, green sago shoots can be collected under winter ice, presumably in deeper waters (Hammer and Heseltine 1988). Turions are perennial diaspores formed underwater and take several weeks or months to develop. The fruit-like seed (drupelets) can require a stratification period to germinate well in areas of fairly mild climate. These findings, plus the observation that sago could not compete well in shallow water against species that produce seeds (annual diaspores) more quickly, led Van Vierssen and Verhoeven (1983) to consider sago a species rather intolerant of habitat desiccation.
In mild climates sago can be evergreen (Spence et al. 1979b). Rarely, some deepwater forms of sago grow perennially from submersed rootstalks and can also have green shoots that survive winter (Moore 1915). Sago can behave as an annual by dying under conditions of high salinity and regenerating from drupelets when salinity decreases (Congdon and McComb 1981). When sago is compared to Potamogeton nodosus, a species that forms winter buds rather than turions, both species invest about the same amount of photosynthate in perennating structures, but sago produces about twice as many propagules (Spencer and Anderson 1987).
The functional aspects of sago's ability to thrive and survive in a wide variety of environments have been addressed in detail by Van Wijk (1988) and will be discussed in later chapters. Van Wijk (1988) points out the confusion that has resulted from use of the terms annual and perennial to categorize plant types as well as life-cycle types, and argues that they should only be used to indicate life cycles of populations without implying a classification of plant species. Under this system, sago could theoretically be said to have an annual life cycle with either (1) generative reproduction by seeds or vegetative reproduction by turions or thickened rhizomes or (2) a perennial life cycle with vegetative reproduction by whole plants or shoots. Not all of these strategies have been observed in nature.
In Europe, the Potamogeton pectinatus association is often linked to brackish water (den Hartog 1963) and inland marshes and depressions affected by mineral pollution (Meriaux 1978). den Hartog (1981) placed sago with a small group of plants that share many properties with marine angiosperms but cannot compete well with them except under special circumstances. He termed sago a member of the eurysaline group of plants in that they are able to tolerate waters from fresh to hyperhaline that vary greatly in chemical composition. These plants are also able to withstand rapid and considerable fluctuations in salt content of the waters they inhabit., Iversen (1929) included sago in a group of species restricted to alkaline waters. Lohammar (1938) found sago in lake waters characterized by both high pH and calcium content. Further analysis of Lohammar's data by Hutchinson (1975) showed sago to be a eurytopic species able to tolerate a wide range of nutrient (nitrogen, phosphorus) concentrations. Moyle (1945) placed sago in an assemblage of hard water species able to withstand waters high in sulfate ion. Other classifications based on water chemistry have been proposed by Spence (1967) and Seddon (1972).