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controlled with the final clean up of a few remaining plants in the autumn of 2010. The Tamarix <br />invasion location will be monitored throughout the summer to be sure no more plants appear. Such <br />monitoring will likely need to continue for a few more years so prolonged seed dormancy effects do <br />not bring back the infestation. <br />Canada thistle has shown a significant decline as a result of control efforts. It is still found in <br />several areas and a few new colonies have been found. However, it appears the control efforts are <br />beginning to beat back its explosive growth and expansion in 2009. <br />The native grasslands continue to exhibit rapid expansion and continued recovery from the <br />removal of grazing. Density has continued to increase in the uplands and the numerical prevalence of <br />annual grasses such as cheatgrass (downy brome) continues to decline. The density of spurge also <br />declines as a result of both control efforts and increased competition from natives. Spurge is still <br />common, as it always will be on this site, but its dominance has declined remarkably in response to <br />increased competition by native species. <br />Unfortunately, in some areas where spurge was formerly very abundant and was reduced by <br />chemical and biological controls now seem to have a new problem weed attacking. In these locations <br />musk thistle and close relatives (the ones with the big magenta flowers) appear to have taken over. In <br />previous reports this was stated to be a risk as a result of the reduction of spurge. In some places these <br />thistles have become particularly dense and are affecting the natural vegetation. Fortunately, this <br />problem is not common on mined areas, but there are still a few large patches even there. Most of the <br />invasion of these species is more on the flat bottomlands east of the forest and south of the former <br />ranch headquarters. There the thistles have become as dense as the spurge ever was. If these areas are <br />controlled with herbicide then seeding must occur after treatment to close the habitat holes into which <br />these opportunistic species invade. Until the grass component can be increased in these areas the land <br />will likely enter into a weed dominant cycle where one species is dominant for a few years and that is <br />replaced by another species. Eventually, it will go back to the original weed species and start the cycle <br />all over again. By densely seeding the area with aggressive natives such as western wheatgrass the <br />cycle steps can be disrupted and the resources that encourage weed invasion will be diverted to <br />utilization by more desirable species. <br />Two of the five new riparian exclosures were quantitatively sampled in early fall of 2010. <br />Analysis of the data and comparison to previous data showed continued gains in growth. The <br />protection of the trees has reaped considerable benefit with woody biomass continuing to increase <br />The large gains in 2007 and 2008 were not generally seen as the vegetation has clearly reached a <br />developmental plateau that is density restricted. Until density declines through environmental <br />selection, rapid gains in height will be limited to areas where the density restricted plateau has not <br />been reached. In fact, the density is so great in Exclosure 1 and to some extent in Exclosure 2 the <br />sampling method will need to be changed because the older approach of laying transect lines is <br />physically impossible to do with sufficient accuracy without damaging the vegetation. <br />Overall, the bottomland vegetation at the end of the 2010 growing season was about as it was <br />at the end of 2009. There is a continued slow decline of the oldest cottonwoods, but with a new <br />generation rapidly gaining along the stream those losses are of less significance. It is sad to see the old <br />and often beautiful giant cottonwoods slowly dying off, but that is the natural process in these riparian <br />forests and there is nothing that can be done about it. <br />Exclosures 3, 4, and 5 were not sampled, as approved by the Corps. However, they were <br />photographed again from the same locations as prior years. A comparison of 2010 to 2009 <br />photographs of these exclosures showed continued, but slowing, development of the riparian <br />vegetation. The decline in the rate of development was completely expected as these vegetation units <br />Status report for 2009 due July 15, 2010 Page 2 of 13 <br />