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<br />Index of Threat = (1- C) * P, where... <br />P =prevalence =the number of ponds containing species A <br />divided by the number of ponds in which the most prevalent fish <br />species (X) occurs, so P = #A / #X; we divide by the most <br />prevalent species to scale P to a maximum of 1, realizing that some <br />ponds are fishless <br />C =control =the number of ponds in which species A occurred <br />that have received a control treatment (poison, screen, etc.), <br />divided by the number of ponds in which species A occurs, so C = <br />#Acontrolled / #A ~I <br />Example: if species A is present in 20 ponds, and species X (the most prevalent species) <br />is present in 40 ponds, the prevalence of species A is calculated as P = ZO,~'/ 40 or 0.5. Further, if <br />10 of the 20 ponds containing species A have been treated to effectively control nonnative fish <br />abundance or escapement, the relative control of species A is C = 10 / 20 or 0.5. Therefore, the <br />overall threat of species A (the proportion of uncontrolled ponds containing species A multiplied <br />by it's prevalence in the study area) is Index of Threat = (1- 0.5) = 0.5 or 0.25. Comparatively <br />speaking, if the number of ponds treated to control nonnative fish increases, and some or all of <br />these ponds also contain species A, the Index of Threat will decline. If the number of ponds <br />containing species A increases due to additional sampling, invasion or stocking, the index will <br />increase. Now two examples will briefly show the integrity of the Index of Threat by defining <br />the endpoints. Theoretically, if effective control has occurred in all ponds that contained species <br />A, then C = 20 / 20 = 1; therefore, the Index of Threat = (1-1) * 0.5 =ZERO. So, as expected, <br />no threat is perceived if control in complete. Also, if species A exists in all ponds and control is <br />zero, C = 0 / 40 = 0; P = 40 / 40 = 1; therefore Index of Threat = (1 - 0) * 1 = 1. Thus, as <br />expected again, the maximum threat to critical habitat would be perceived by a prevalent <br />nonnative fish species occurring in all ponds, and no control measures have been applied. <br />Pre- and Post-Regulation Fish Stocking Data <br />The goal of this effort was to compile data on nonnative, nonsalmonid fish stocking in <br />western Colorado for the years 1998 to 2001. It was decided that 1998-1999 would serve aspre- <br />regulation data, and 2000-2001 would represent post-regulation data. Although new stocking <br />regulations were adopted early in 1999, it was understood that the remainder of the year would <br />be required to make the private sector, vendors and purchasers of nonnative, nonsahnonid fishes, <br />aware of these new restrictions. Available data was sought or acquired from five categories of <br />records believed to document stocking activity. <br />1) Vendor sales receipts <br />2) CDOW private stocking permits <br />3) CDOW importation permits <br />4) CDOW private and commercial lake licenses <br />5) CDOW stocking records for public waters <br />6 <br />1 <br /> <br /> <br /> <br />J <br /> <br />v <br />1 <br />L~ <br /> <br /> <br /> <br />f <br /> <br /> <br />i <br /> <br /> <br />