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A Natural Areas Inventory of the - Kansas Natural Heritage Inventory ...

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CHAPTER 2. NATURAL COMMUNITIES<br />

2.1. INTRODUCTION<br />

Hillary Loring<br />

<strong>Kansas</strong> Biological Survey<br />

2101 Constant Avenue<br />

Lawrence, KS 66047-3759<br />

hillaryloring@netscape.net<br />

Freeman et al. (1997) documented nine kinds <strong>of</strong> natural communities on FLMR: four forest types<br />

(Maple-Basswood Forest, White oak-Shagbark hickory Forest, Cottonwood-Sycamore<br />

Floodplain Forest, and Pecan-Sugarberry Floodplain Forest); two herbaceous types (Big<br />

bluestem-Indian grass Tallgrass Prairie and Bulrush-Cattail Marsh); one sparse vegetation type<br />

(Limestone Caprock Butte Sparse Vegetation); and two riverine types (Glaciated Region<br />

Headwater and Big River). Their surveys confirmed that FLMR supports several large and<br />

globally significant forest remnants. Floodplain forests on <strong>the</strong> installation were believed to be<br />

<strong>the</strong> largest old-growth stands remaining in <strong>the</strong> lower Missouri River valley. Upland forests and<br />

smaller natural communities associated with <strong>the</strong>m were determined to be regionally important.<br />

Collectively, <strong>the</strong>se natural communities were found to provide habitat for nearly two-dozen<br />

globally rare or state-rare species and support a rich biota characteristic <strong>of</strong> <strong>the</strong> forest-grassland<br />

ecotone.<br />

Surveys undertaken in 2003 updated earlier studies by: 1) re-examining <strong>the</strong> boundaries <strong>of</strong> <strong>the</strong><br />

significant community types; 2) ga<strong>the</strong>ring additional species composition and cover data to<br />

permit more accurate characterization <strong>of</strong> <strong>the</strong> community types; and 3) searching for and<br />

describing previously unreported, exceptional natural areas on <strong>the</strong> installation. It should be noted<br />

that surveys conducted in 1995–1996 occurred soon after <strong>the</strong> massive floods <strong>of</strong> 1993. The<br />

disturbance, seed dispersal, and flood-induced germination associated with that event likely<br />

caused significant and continuing changes in <strong>the</strong> distribution, composition, and structure <strong>of</strong> <strong>the</strong><br />

floodplain forest communities. It was hoped that our follow-up studies would help characterize<br />

<strong>the</strong>se changes.<br />

2.2. METHODS<br />

During <strong>the</strong> 1995–1996 field seasons, vegetation samples were obtained from six upland sites and<br />

14 floodplain sites, all dominated by forest vegetation. Four plots were established at each site<br />

for a total <strong>of</strong> 24 sample plots on <strong>the</strong> uplands and 56 sample plots in <strong>the</strong> floodplain. Our hope was<br />

to resample each plot in 2003, but many <strong>of</strong> <strong>the</strong> plot markers could not be located, apparently<br />

having been removed by floods or humans. New plots were established as close as possible to<br />

<strong>the</strong> old plots.<br />

Six upland sites (AA through FF) and 23 floodplain sites (A through W) were sampled (Figure<br />

NATURAL AREAS INVENTORY OF FT. LEAVENWORTH II 13

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