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<br />2.2 <br /> <br />3. the extent to which this technique might be developed <br />for covariate analysis of randomized seeding experiments. <br /> <br />(b) <br /> <br />Background: <br /> <br />1. Variability of Seeding Chemicals in Precipitation. <br /> <br />In earlier investigations in the Pyramid pilot Project (1977), it was <br />shown that the silver content of the snow falling in the target area (east <br />of the Sierra crestline), varied considerably with time throughout the con- <br />tinuous seeding period at'any one sampling site. It was also shown by <br />Warburton (1973) that the highest silver contents (from the silver iodide <br />seeding) occurred when the precipitation crystal types were predominantly <br />needles and columns. Since these crystal types are produced predominantly <br />in the warmer temperature ranges (-30C to -80C), it seemed reasonable to <br />suggest that the principal water capture and growth of these crystals had <br />occurred in the lower elevations. This is consistent with the later obser- <br />vations from aircraft that frequently there is very little liquid water in <br />the winter clouds over the Central Sierra Nevada above 12,000 ft elevation. <br /> <br />Later studies of the chemistry of snow were conducted by Warburton, <br />et al., (1979) and by Stone and Warburton (1981). The results of this work <br />showed that seeding chemicals (silver) and often special tracer chemicals <br />(indium and cesium) appear in the snowfall in temporally and spatially <br />confined manners. This evidence was obtained by two separate sampling <br />techniques, time sequential and vertical profiling. The time sequential <br />sampling method requires personnel to be located at the sampling sites <br />during snowfall events. The profiling method is normally used between <br />storms in fair weather. Both give similar information but real-time <br />sampling has the advantage of being able to collect ice crystal structure <br />information simultaneously. <br /> <br />The chemical analysis data from both sampling techniques have led to <br />the same basic conclusion, i.e., that the seeding agent from both ground- <br />based or airborne seeding systems appears in the snow only 10% to 30% of <br />the time during which seeding is conducted. <br /> <br />These results imply that seeding 'plumes' are spatially confined even <br />at distances of 70 km downwind of the release sites. Although the plumes <br />may be located over a given sampling site for periods of time ranging from <br />zero to twelve hours throughout a continuous seeding event, on the average, <br />the target area is not receiving seeding aerosol material in its precipita- <br />tion for 70% to 90% of the seeding period. <br /> <br />Because of these results, we plan to conduct a program of research <br />aimed at developing a new method for assessing the effects of seeding based <br />upon trace Chemistry. <br /> <br />I <br />I <br />I <br />I <br />I <br /> <br />I <br />I <br />I <br />I <br />I <br /> <br />I <br />I. <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />