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<br />5 <br /> <br />than predicted. The apparent increase for tho combined 12 cases was 104 per cent. <br />Application of Students T test grwe a 0.995 confidence level. The actual increment <br />was 1200 acre-feet (1.48 x 106 cubic metres). . <br /> <br />21. The more usual circumstance is that storm flows are too difficult to <br />separate accurately, requiring' longer time ]Jeriods to be chosen for flow averaging. <br />The week and month are usually too short to provide a stable number of storm occur- <br />rences, but in some places seasonal precipitation can be used. This is most suitable <br />where the precipitation which provides the bulk of the annual water supply occurs in <br />the winter months as in Mediterranean climates. Where significant amounts of <br />precipitation occur throughout the year, the annual floH is best suited for use. <br />The usual practice is to average the flow over the water year which runs from 1 <br />October to 30 September (for many areas, th(~ auturllJl period offers a low point in <br />hydrological activity so that dividing a major river rise into 2 parts for distri- <br />bution into 2 water years is not a frequent problem). <br /> <br />22. Al though annual flovl has usuall~f 'been used as the ba:o,is for evaluating <br />non-randomized experiments, it is possible '\;0 rand,omize seeding by years, The <br />resul ting eval ua tion ,1ill be credible if the seeded years exhi bi t a marked departure <br />of runoff compared "\Vi th that of the unseedec, yeaTS without benefitting from a lareer <br />number, or lillusually heavy, storm events. Grant, et al., (1971), reported use of <br />this approach in evaluating seeding in the \'Tolf Creek Pass region of Colorado. The <br />experiment ran from 1965 to 1969, with seeding of all storm events eluring the years <br />1965, 1967 and 1969. No seeding was done in 1966 or 1968. The indicated inc:r;ement <br />of flow from the three target river basins was 228,000 acre-feet (2.8 x 108 m'). <br />Mielke, et a1., (1977), have recen-t1y published a cor:rection stating that 1970 Has <br />an unseeded year. <br /> <br />23. The estimates of increase derive froll! a statistical regression relating <br />the streamflow in the target area (San Juan River gauged at Pagosa Springs, drainage <br />area 772 km2; South ]'ork Rio Grande Hi vel' near South ]'ork, drainage area 559 km2; <br />and the Alamosa Creek above "J~errace Reservoir, drainage area 277 km2), to that from <br />the control area (Piedra River near Piedra, drainage area 961 km2; Animas River at <br />Howardsville, drainage area 145 km2; and Lake Fork of the Gunnison River at Gateview, <br />drainage area 865 km2), for a historical pel:'iod of 26 years. The correlation <br />coefficient of target area streamflo11 to control area streamflovl was 0.97. 'rhe <br />probability of the comb:i.ned seeded streamflo"\V being observed by chance is 0.005. <br /> <br />24. Of the various statistics 'v,'hich might serve to differentiate between <br />effective and. ineffective seeding, Narkovic (1966) identifies the mean a.nd the <br />variance as the statistics of choice in testing for significance. Effective seeding <br />would apply to seeding associated ,ii th an increase in streamflo"\V; seeding wh.ich <br />produced no increase 'Iiould be considered ineffective. <br /> <br />25. There have been hlO basiC approaches used to estimate the effectiveness <br />of cloud seeding in increasing the mean flow from the target area. The first <br />invol ves comparisons of target area flow following seeding wi th target area flo"l in <br />the absence of seedinG" Thi~: type of comparison has usually been made by comparing <br />a few years of seeded experience with the flo\'l observed over the years beforl~ seeding <br />was undertaken. The validi t;y of such a comparison ,.is heavily dependent on the vari- <br />abili ty of the annual floHS which go to make 1..11) the record. Examination of the <br />stability of past records 'Iiill quickly reveal v]hether or not there have been groups <br />of years in the past .,hich, if they had been seeded, liould have g1ven indications <br />of seeding effectiveness that would be entirel;y' ficti tious. "'hen this is the case, <br />a long period of seeded record is required before much confidence can be placed in <br />the seed/no seed ratio. The number of years required to constitute a "long period <br />of seeded record" ,'lill depend. on the variability of streamflo,'lfrom year to '(ear <br />. before and. afte:c seeding is undertaken. Five years of seed.ing could easily ;~oincide <br />a fortui taus wet l)eriod. Ten-year seeding programmes 'liould be much le:3s to bo so <br />easily confounded. <br /> <br />