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transport ways and commercial and residential structures during early <br /> expansion was also relatively unregulated compared to modem standards. <br /> These developments were also relatively small-scale and somewhat <br /> reversible compared to modem developments. <br /> 2. Existing threats-The location of residential and commercial development <br /> and construction are under the jurisdiction of local city and town zoning <br /> ordinances. The City of Denver, located in what was once prime habitat <br /> for Z. h. preblei, is primarily zoned for commercial and residential <br /> development. Similarly, much of the Cities of Boulder, Fort Collins, and <br /> Greely are commercially and residentially zoned. Fortunately, the City <br /> of Boulder has exercised great foresight through the purchase of extensive <br /> parcels of land, placed under the jurisdiction of the Open Space <br /> Department, to be used primarily as natural, recreational parks or for <br /> ecologically sound agricultural purposes. No such effort has been made <br /> to date by the Cities of Fort Collins and Greely. Much of the intervening <br /> lands between these major cities is zoned as residential and agricultural. <br /> However, the towns of Loveland and Longmont, and dozens of other <br /> smaller towns, fragment much of the intervening landscape with both <br /> small commercial and generally expanding residential zones. In addition, <br /> there are currently no effective zoning ordinances that provide for a <br /> buffer zone, or in any other way protect critical meadow and riparian <br /> areas from grazing. Without the active participation and commitment of <br /> town and city planning committees to establish local zoning ordinances <br /> that preserve locations of contiguous, natural habitat, the remaining <br /> critical habitat of Z. h. preblei will surely eventually perish. <br /> 3. Potential threats- Continued residential, commercial, municipal and <br /> agricultural developments could potentially threaten the remaining critical <br /> habitat of Z. h. preblei. <br /> IL Assessment and Recommendations <br /> 1. General assessment of vigor, trends, and status- The assessment of historical trends <br /> concerning the vigor and status of Z. h. preblei is a difficult task, due to both the <br /> historical and current paucity of demographic data. Historical data in the form of study <br /> skins outlines the historical range of the species (see Geographical range). However, the <br /> status of the species within its historical range is not well known, as few study skins have <br /> been collected (a total of 38, with 14 other records in Colorado, and a total of 6, with 1 <br /> additional record in Wyoming). Armstrong (1972) stated that this subspecies, "is poorly <br /> known in Colorado, an apparently is nowhere abundant." Long (1965) echoed this idea <br /> for Wyoming in stating that this subspecies was rare. These assessments may provide an <br /> accurate portrait of the general vigor of this subspecies. It may be that Z. h. preblei has <br /> historically maintained a low population density in Colorado and Wyoming,or has at least <br /> been isolated in its distribution to refuges of critical moist, lowland habitat. Since there <br /> is evidence that this subspecies still exists in locations with appropriate habitat (i.e, Coal <br /> Creek in 1989, Rocky Flats in 1991, and VanVleet in 1992), the extinction of the species <br /> may not be imminent. However, given the number of reports of this subspecies in recent <br /> history (12 individuals in the last 20 years), and the nature of the reports (found in <br /> isolated refuges of critical habitat), the current status of the species may be declining, and <br /> the preservation of refuges of critical habitat may be essential to maintain this subspecies. <br /> Fm.l S1 S u <br /> amp Ecs,In. <br /> March 24.1993 7d <br />