4 grasses. The practical issue is that in ecological communities some species are always common, while most are always infrequent or rare. To maximize prairie biodiversity, a variety of species abundance distributions should be promoted. A short-term strategy would increase richness by depressing dominance; a mixture of fire intervals, seasonal burns, grazing frequencies, and grazing intensities by different animals should produce the maximum species diversities within and between habitats. A long-term strategy including historically plausible growing-season burns and grazing should favor some species now eclipsed by large C4 dominants. The point is to avoid uniformity of treatments that artificially simplifies what probably was once a far more varied set of communities that now exists. Howe recommends some useful principals might include: (1) managers may use varied fire and feasible grazing regimes to decrease total dominance and promote short-term increases in species richness, and (2) some treatments should encourage increases in abundance of native early-season and other species in a long-term strategy to favor plants currently suppressed by large C4 dominants. Howe stresses that the goal should be to develop scientific rationales for restoration and conservation, rather than rely on unexamined convention." />
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Managing species diversity in tallgrass prairie: Assumptions and implications

    • Authors: H. F. Howe

      Date: 1994

      Journal: Conservation Biology

      Volume: 8

      Number: 3

      Pages: 691-704

      Summary of Methods: In this paper, Howe argues that history, recent experiments, and theory suggest that there is little compelling scientific argument for conservation or re-creation of a monotonous "tallgrass type". Historical and experimental evidence suggests that tallgrass assemblages should be diverse, different from each other, and dynamic. Short-term manipulation of species abundance distributions and long-term use of historically plausible burn and grazing regimes may conserve or re-create a more species-rich tallgrass assemblage than would encouragement of consistent domination by a few C4 grasses. The practical issue is that in ecological communities some species are always common, while most are always infrequent or rare. To maximize prairie biodiversity, a variety of species abundance distributions should be promoted. A short-term strategy would increase richness by depressing dominance; a mixture of fire intervals, seasonal burns, grazing frequencies, and grazing intensities by different animals should produce the maximum species diversities within and between habitats. A long-term strategy including historically plausible growing-season burns and grazing should favor some species now eclipsed by large C4 dominants. The point is to avoid uniformity of treatments that artificially simplifies what probably was once a far more varied set of communities that now exists. Howe recommends some useful principals might include: (1) managers may use varied fire and feasible grazing regimes to decrease total dominance and promote short-term increases in species richness, and (2) some treatments should encourage increases in abundance of native early-season and other species in a long-term strategy to favor plants currently suppressed by large C4 dominants. Howe stresses that the goal should be to develop scientific rationales for restoration and conservation, rather than rely on unexamined convention.

      Article Summary / Main Points: None

      Vegetation Types:

      MLRA Ecoregions:

      Agrovoc Control Words: Riparian zones Rangelands Wildlife

      Article Review Type: Refereed

      Article Type: Scientific Opinion

      Keywords: tallgrass prairie, grazing, species diversity, conservation

      Annotation: None

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