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. i <br /> 16 <br /> in theae calculations. Plants that wnrn not idantiliabla to <br /> species and that had a ranqe in WIS ratings were assiqned <br /> the everaqe for the ranqe of WIS ratings. An example oP a <br /> WMI calculation is provided below. <br /> Eseentially, a wMI assiqns a WIS to the community by <br /> wniqhtinq each apecies' WI3 by ita relative cover. The WMI <br /> provides an objective parameter useful in desiqnatinq a <br /> plant community as watland or upland. Fiqure A.1 shows n <br /> braakdown of the WMI scale. Idanlly, the "bra�kpoint" <br /> batween wetland and upland vagetation ia a WMI of 3.0 (i.e. , <br /> FAC) , with wetland bainq less than 3.0 end upland ba!nq <br /> qreater than 3.0. However, a WMI closa to 3.0 impliae a <br /> qreat deal of uncertainty in makinq a watland detarminetion. <br /> Whan the WMI is neer 3.0, vegetation may not be claarly <br /> indicative of either wetland or upland. However, as tha WMI <br /> of a plant community or plot approaches the extremns of the <br /> scale (i.e. , 1 ur 5) , the probability of the vegetation <br /> beinq indicative of either wetland or upland increasas. An <br /> inve6tiqation of tha suitability of this methodoloqy for a <br /> wide variety of plant communities in difPerent portions of <br /> the U.S. was carried out by Wentworth and Jchnson (1966) and <br /> should be referred to for more informatlon. <br /> Usinq both tha percentaga of the dominant apacias that arn <br /> FAC or wetter and a WMI providea en objective method f�r <br /> datermininq whather the veqetation of a community is adapted <br /> to wetland or non-wetland conditions. However, both of <br /> these indicea, or quidelines, are only ae qood as the <br /> classlfication syatem on which they are based. Inaccuracies <br /> of the WIS assignments will be reflected in the indicas. In <br /> casee where inconsistancy occure batwaen a epecies� WIS and <br /> its ecoloqical niche, based on field obaervation and <br /> apparent soil and hydroloqical conditions, veqetation <br /> indices may need to be evaluated more critically. <br /> All the plant communities on tha property were further <br /> classified according to the predominant vegetative growth <br /> form, and in some cases, substrate material, floodinq <br /> reqime, and;or landuse. Wetland communities were clasdified <br /> according to a eystem developed by Cowardin et al. (1979) , <br /> while upland communities wera clasaified accordinq to the <br /> � system described by Anderson et al . (1976) . <br />