Laserfiche WebLink
2001 was 15.68 inches. This represents a 42 percent increase from the January-July <br />average of 8.89 inches, a 36 percent increase from the September-July average, and <br />• increases of 81 percent (January-July) and 62 percent (September-July) from the <br />corresponding periods in 2000. <br />VEGETATION COVER <br />In general, total vegetation cover values were higher this yeaz than in 2000. This can be <br />attributed to greater precipitation during the spring and summer of 2001. The early and <br />heavy precipitation in April and May of this year promoted eazly green-up and growth of <br />the cool season vegetation within the reclamation azeas and reference azea. Heavier than <br />normal precipitation in July 2001 promoted new growth in the warm season species as <br />well as continued growth in the cool season species. Competition from annual and <br />perennial cool season species may have reduced growth and flowering in the warm season <br />graminoids this season. For the purposes of direct comparison, quantitative cover data is <br />present (Table 11) for the 1995 and 1997 reclamation areas and the 1998 reseeded or <br />interseeded azeas (1998-2001) and the Osgood sand reference azea (1994-2001). <br />As has been noted previously, the scale of the response to the increase in precipitation <br />varies significantly between the reference azea and the reclamation areas. Osgood sand <br />reference azea total vegetation cover increased 36 percent (35.80 to 48.80%) from the <br />2000 growing season, while the reclamation azea total vegetation cover increase over the <br />2000 growing season ranged from 17 percent (1998 reseeded and interseeded azeas) to 88 <br />percent (1995 reclamation azeas). This may be attributed to the difference in lifeform <br />• dominance in each of these communities or the opportunistic nature of several of the <br />annual species. <br />Interestingly, the variability of vegetation cover, as reported by the standard deviation of <br />the mean for each area sampled remained nearly the same between the two yeazs (2000 <br />and 2001). This chazaderistic appears to be more related to the age of the vegetation <br />stands than other pazameters, with the Osgood sand reference azea showing the lowest <br />mean variation and the 1998 reseeded and interseeded azeas showing the greatest <br />variability with the 1995 and 1997 reclamation areas intermediate in value between these <br />extremes. <br />Mean total vegetation cover was variable this season ranging from 38.60 percent to 51.00 <br />percent. The area exhibiting the lowest mean total vegetation cover during the 2001 <br />sampling were the 1997 reclamation azeas with 38.60 percent total vegetative cover. The <br />1998 reseeded or interseeded azeas exhibited the highest level of total vegetation cover <br />with 51.00 percent. This result is not unexpected given the fact that the 1998 azeas had <br />been previously seeded to the permanent revegetation mix and some mature growth had <br />already developed. Further, the 1998 reclamation areas contained the largest average <br />cover of Bromus tectorum. Significantly, in those pazcels within the 1998 azeas where the <br />controlled burning occurred, cover sampling revealed Bromus tectorum cover was non- <br />existent (west of dugout) or greatly reduced (south of sediment pond), while cover of <br />desirable perennial gasses wasincreased. <br />• <br />-17- <br />