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Because of the difficulty and inherent danger in accessing the base of the mine bench outslopes, the planting was conducted near the mazgins of Dutch Creek. This azea was selected in order to minimize sediment contribution from areas adjacent to the creek, and to help stabilize the channel. Prior to planting, the students were taught the importance of establishing plant communities as part of the reclamation and stabilization process. Over 1,000 trees and shrubs were planted by the students. Education The annual meeting of the National Association of Abandoned Mined Land Reclamation Programs was held in Steamboat Springs, Colorado in September, 2000. A paper was presented by the Division which discussed reclamation at Coal Basin. The paper emphasized the mine bench outslope revegetation effort, and the observations made during the preceding summer. The presentation included a discussion of the predicted project outcomes and suggestions for future project modifications. Measurement of Success In order to ascertain some measure of project success, direct sampling of the stream systems in Coal Basin was abandoned and evaluation of sediment yield from the individual outslopes was to be based upon sediment yield. A model recommended by the U.S. Geological Survey was evaluated in 1999 and 2000. Data from the model is presented in Tables 3, 4 and 5 at the end of the report. The model estimates sediment yield based upon observations of vazious physical pazameters encountered at a given outslope. Factors such as slope stability, vegetative cover, geologic and soil chazacteristics, and gully flow dynamics aze evaluated. A scoring system was developed based upon the evaluation of the observed characteristics. An estimation of sediment yield is then established based upon the rating given to an individual outslope. As one or more factors change relative to other factors, the sediment yield estimation is revised as the rating for the basin conditions change. It is important to note that we view this model as a means to evaluate relative erosion potential at the various mine bench outslopes, rather than as a definitive measurement of sediment generation. Therefore, actual rates of erosion and resultant sediment yield aze not reflected in the model. 2004 Stabilization Project Site monitoring through the 2003 growing season indicated that the percent of vegetative cover was less significant than what was desired in order to sufficiently stabilize the outslopes. Therefore the Division determined that a second attempt at establishing vegetation at the outslopes would be made in the fall of 2004. In order to finance this effort, modifications to the Non-Point Source grant were made, including provision for additional funding. Construction A contract was bid in the summer of 2004. This contract contained many of the project specifications completed in 1999. Hand crews constructed approximately 3,500 small