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<br />001220 <br /> <br />VIII.4 <br /> <br />In somewhat different context, a "saturated watershed" has been <br />taken to denote minimum potential infiltration and maximum potential <br />runoff; this particular expression has been misused grossly. In <br />mountain and foothill watersheds, all the soils probably are never <br />saturated simultaneously. No less an authority than R. E. Horton <br />states that, even with the heaviest prolonged rainstorms, the water <br />content of soil generally becomes very little more than field capacity, <br />Probably this is true of permeable, coarse textured soils on slopes <br />and ridge 'crests. In the same watersheds, however, the soil adjacent <br />to channels may become nearly saturated. <br /> <br />The phenomena of soil-water flow, under conditions of saturation <br />and partial saturation, are far more complex than those of floW in <br />open channels. They may prove amenable to experimental analysis using <br />new radioactive-tracer techniques, but even these techniques are by no <br />means unquestionable, Certain tracers are adsorbed strongly by mineral <br />particles or organic matter in the soil. Acceptable dosage of the <br />environment and permissible dosage of personnel may greatly lessen <br />effectiveness; Beyond these and other limitations'of procedure, the <br />. flow paths in the soil may be so diverse that mean flow time is unique <br />to the particular experiment. In other words, results cannot be trans- <br />posed to ':,other areas or extrapolated to other soil-water conditions. <br />Even so, tracer techniques promise to tell us something about soil-water <br />movement in aspects of hydrology that have been expressed nebUlously as <br />"interflow", "quick seepage", "storm flow", "soil-water contribution to <br />ground-water recession", and so on. <br /> <br />Methods of measuring soil water <br /> <br />Periodic sampling of the soil <br /> <br />Of those commonly used for determining the water content of soil, <br />the gravimetric method is considered the most accurate. The standard <br />procedure is to remove soil samples in the field from desired depths <br />with soil tubes or augers, and to place them inmiediately in sealed <br />containers which then are weighed, opened, contents dried at 10So C, <br />and reweighed. The loss in weight represents soil water,. commonly <br />computed as a percentage of the weight of dry soil. <br /> <br />The gravimetric method has several disadvantages, including I <br />(1) beoause each sample is removed from the ground, subsequent change <br />in water content of the soil cannot be determined by re-sampling at <br />precisely the same point; (2) the sample is relatively small in volume <br />and, because soils in the field usually are decidely non-homogeneous, <br />may not represent mean water content of the soil at the designated <br />depth over all the area of interest; (3) usually at least 24 hours <br />elapses before analytical results are available; and (4) considerable <br />equipment and labor are involved. <br /> <br />