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Conceptualizing mountains as water towers is an important cornerstone of modern hydrological research. Mountainous areas, which comprise only a small percentage of the Earth’s surface, supply many surrounding arid and semiarid lowlands with water for irrigation and food production (Messerli et al., 2004) as well as many other services (e.g., hydropower, ecosystem health, recreation, etc.). The distribution of runoff in mountain environments is highly disproportionate to that of lowland areas (Viviroli et al., 2007) and consequently, demand for runoff is often highly contentious. Monitoring snowpack and determining snow water equivalent (SWE) have become important factors for assessing annual variability and predicting runoff availability (Coughlan & Running, 1997; Rango et al., 1977). Many SWE models use coarse climate data that have been interpolated, downscaled, or extrapolated to make predictions at finer scales (Wilby et al., 1999; Wood et al., 2004). Although climate data are capable of enhancing SWE predictions, error associated with interpolation, downscaling, and extrapolation can greatly reduce prediction accuracy. To overcome the limitations associated with climate data, many SWE models also require extensive field data. However, field data require considerable time and capital which are not always available to local resource managers. Consequently, local resource managers are unlikely to generate the most accurate prediction of annual runoff.
Snow covered area (SCA) is a primary input in SWE models and is important to both local water resource managers estimating SWE, as well as winter and summer recreationists in mountain areas. Tourism, not often at the forefront of hydrologic or environmental research, supports many mountain communities that capitalize on recreation associated with snow cover and snowmelt. Climate change may result in a decrease in natural annual snow cover. As a result, ski resorts may need to supplement natural accumulations with artificial snowmaking (Scott et al., 2003, 2006; Steiger & Mayer, 2008; Vanham et al., 2009). Non-winter activities such as fishing and white-water recreation (Mickelson & Hamlet, 2008) are also important to mountain communities and are directly related to snow cover and runoff. Consequently, SCA is important to both water and recreation resource managers in mountainous regions.
Early monitoring of SCA utilized ‘hard’ image classification (Dozier, 1989; Rango & Itten, 1976), which introduced error into classification outputs when multiple land cover classes were present in a single pixel. In an attempt to distinguish different land cover classes at the sub-pixel level, land cover classes were evaluated using spectral unmixing, which provided a deterministic method by which multiple discrete spectral signatures were identifiable in individual pixels (Vikhamar & Solberg, 2003). A more inductive method of performing sub-pixel classification, fuzzy classification, has rarely been used in SCA assessment. The objectives of this study were to (1) assess the capability of fuzzy classification to approximate fractional snow cover, (2) examine the sensitivity of fuzzy fractional snow cover predictions to small changes in environmental parameters between years, and (3) develop a cost effective, simple method of estimating SCA for resource and recreation managers who do not have access to extensive academic or governmental resources. We utilized free data sources as well as a combination of both common commercial and free software packages to achieve our objectives.