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(1) No detectable change between post-fire bulk densities within the burn area and the controls at the first burn site (the old road bed). However, this site did show significantly higher bulk densities than the second burn site (approximately 1.5 gm/cm3 vs. 1.3 gm/cm3) and comparison to the controls at the first burn site indicated that only the upper 2 - 5 cm of the old road were compacted relative to the surrounding (less disturbed) areas. Both burn sites showed bulk densities that increased with depth. Samples obtained at pre- and post-fire within the burned area at the second burn site indicated that bulk density increased from about 1.1 gm/cm3 to about 1.3 gm/cm3; however, comparisons between the controls and burned area did not show any statistically significant difference. Therefore, results at the second burn site are suggestive, but not conclusive, of an increase in bulk density as a result of the fire.
(2) Thermal conductivity changed significantly, but in an unexpected way, at both burn sites as a result of the fires. Regressing the measured thermal conductivity against the corresponding bulk densities and soil moistures (i.e., λ = Aρb+BΘv) for the controls and burn areas yielded: λcontrol = 0.123ρb+8.12Θv and λburn = 0.486ρb+2.70Θv. Although no unambiguous change in bulk density was detectable at either burn site, both sites showed that thermal conductivity to be about 4 times more sensitive to bulk density after the burn than before. On the other hand, thermal conductivity appears about a third less sensitive to soil moisture after the fire than before. These results would seem to indicate some change in soil structure as a result of the burns. The nature of these changes is not clear from this particular data set. However, in a semi-arid region, such as Manitou Experimental Forest, where Θv < 0.1 much of the time, present results suggest that the daily and annual soil heating within the burned areas will exceed the unburned areas in both amplitude and depth of penetration.