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Other Scales of Diversity <br />Noss (1990 as reproduced in West 1993) distinguished four levels of biodiversity, with notes an <br />composition, structure, function, inventory, and monitoring_ His regional landscape diversity has been <br />discussed; his ecosystem- community level, despite the nomenclatural ambiguity, is closely allied with <br />Whittaker's alpha diversity. Noss identifies two finer levels of diversity. A focus on species <br />populations, perhaps in deference to wildlife ecologists, forces us to consider whether plant <br />populations and ultimately species composition matter in reclamation. Finally, there is a genetic level. <br />In the final analysis, evolutionary processes take place at the population level where genotype selection <br />occurs. Fortunately, we are unaware of work done to investigate genetically based ecological <br />differentiation in populations arising from mining revegetation. <br />Units for Assessing Diversity <br />To a large extent, diversity indices are attempts to give mathematical expression to our intuition. <br />Botanists are predisposed to immediately conceive diversity in terms of flora. Laypersons and perhaps <br />a good many other orgardsms are likely to look past species and see physiognomy. Physiognomy <br />refers to the gross appearance of a kind of vegetation, ignoring its taxonomic composition. <br />Diversity can be measured using broader taxa (hierarchical diversity) or growth - forms, although like <br />species, growth-forms do not differ equally. Vegetation diversity may be distinguished from species <br />diversity on this basis (Bonham and others, 1980). Elsewhere in these proceedings, Prodgers <br />evaluated some redaination factors using a number of vegetation diversity measurements including <br />hierarchical diversity. The coefficient of determination for species and genera richness was 0.88, so <br />evaluating both was hardly worth the effort. The r for species or genera versus families was a little <br />Iess than 0.5. Growth -form ricimess and taxonomic groupings were less related (r < 0.2). <br />Sindelar (1980) found revegetated communities to have about half the richness of native rangeland and <br />considerably lower heterogeneity, in part due to reliance on introduced species that tended to restrict <br />diversity through competitive dominance. par more recent reclamation, that is no longer the case. <br />Table 1 compares richness of fields (uniform soils and seeding) and pastures (sets of contiguous <br />fields) at Western Energy's Rosebud 1fiine to several semmatural types sampled in unmined areas <br />elsewhere in eastern Montana, <br />In Table 1, ricitness is defined as the number of taxa in sample sets unequal in number but with <br />species area curves indicating adequate floristic inventories. The richness of fields compares <br />favorably to a simple blue grarna/westem wheatgrass community. Species and genera richness of <br />pastures falls within the range of more complex native types, but family richness lags. <br />Structure is the natural complement to composition. Structure refers to the measured and described <br />elements of physiognomy. In physiognomy, the emphasis rests on the overall appearance of <br />vegetation, regardless of its floristic composition. Whereas composition uses species units, structure <br />uses life - forms, which may be grouped into synusias (i.e., a ref nerriart of the "layer" concept, groups <br />of life forms, or subdivisions of physiognomy). The proportion of lifteforms deterorines a plant <br />community's physiognomy. <br />Many animals depend upon the structure oftheir habitat. MacArthur (1964), for example, found that <br />bird speces diversity was accurately predicted by foliage height diversity. This type of functional <br />relationship should guide how structural classes are defined. For the animal ecologist, synusia like <br />those used by MacArthur (herbaceous ground cover, shrubs, and small trees 2 -25 feet tall, etc.) might <br />be best. For the plant ecologist, the building blocks of growth -forms (e.g., Raunlciaer's 1934) may be <br />most appropriate. <br />From a physiognomic viewpoint, most coal revegetation would be classed as grassland, steppe, or <br />scrub types (following the types identified by Daubennmire 1968 p. 251). The addition of a forest or <br />145 <br />