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<br />Forest-Fire Devegetation and Basin Adjustments <br /> <br />hydrophobic layer on the gentler slopes of Burnt Mesa study area. and more <br />extensive remnants of the layer are still preserved on the hillslopes there <br />(fig. 5). <br /> <br />In the late fall of 1977. another change in ground conditions and weather- <br />ing processes resulted in an increase in sediment availability and erosion. <br />Freeze-thaw cycles began in November 1977 as available soil moisture was sub- <br />jected to diurnal fluctuations in surface temperature. Freezing and thawing <br />disrupted the previous ground-surface texture (figs. 7A and 7B). Frost <br />heaving resulted in the upward movement of fine particles relative to coarser <br />ones. Loose. fine-grained sediment was concentrated at the ground surface <br />where minor runoff events could easily remove it. A three- to eight-fold <br />increase in erosion occurred between October and December. 1977. in response <br />to this surface alteration (fig. 8). <br /> <br />Differential rates and amounts of erosion over the watershed are most <br />likely related to differences in soil moisture and consequently, frost-heaving <br />intensity. Variations in erosion on the hillslopes are common along erosion- <br />pin transects; however. all transects showed a dramatic increase in erosion <br />during the freeze-thaw cycles (fig. 8). The intense-burn watershed of <br />Burnt Mesa experienced the greatest amount of erosional response to frost <br />heaving (fig, 8). This is attributed to (1) hillslope aspect (orientation) and <br />moisture regimes. (2) relative proportion of fine sediment in the colluvial <br />cover. and (3) lack of ,extensive vegetational cover. <br /> <br />Seasonal variations in the erosion of the Burnt Mesa watersheds are given <br />in table 4 and figure 6. Erosion rates increased significantly during late fall <br />and spring. These seas~ns coincide with periods of accelerated mechanical <br />weathe!ing (frost heaving:). Erosional stability and periods of low sediment <br />production occur when the watersheds are blanketed with snow (fig. 6). <br /> <br />Other Factors Controlling Watershed Erosion <br /> <br />Erosion measurements given in table 4 suggest that factors other than <br />mechanical weathering inf}uence sediment supply. For example. erosion rates <br />are greater and more variable in the Burnt Mesa area than in the Apache <br />Springs area (table 4). Surface denudation in the Apache Springs area is <br />distributed more uniformly through time than in Burnt Mesa (fig. 6). Rates <br />of revegetation of the watersheds are partially responsible for these varia- <br />tions in erosion. Grass quickly re-established cover over a greater part of <br />the surface in the Apache Springs area than in the Burnt Mesa area. Re- <br />vegetation reduced the amount and variation of surface erosion over time be- <br />cause m~chanical weathering was less ~ffective in the vegetated zon\~s. <br /> <br />Anotl:er vegetational factor influencing the variability of erosion through <br />time is the post-fire needle cast . A needlecast is a thin blanket of pine <br />needles covering the grDund surface which forms when partially-burned trees <br />drop dead needles to the ground (fig. ZB). Needlecasts are common in <br />moderate and light burns. Their occurrence depends on the density of <br />standing conifers. arid of dead. unburned needles. This type of forest <br />litter protects the recently devegetated colluvial cover and reduces erosion <br />(Connaughton, 1935; Megahan and Molitor. 1975). Needlecasts break the im- <br />pact of raindrops and distribute rainfall over the surface. allowing slow in- <br /> <br />211 <br />