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RESEARCH· ·1970·

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B248<br />

HYDROLOGIC TECHNIQUES<br />

type in the upper area. Another 20 percent of the watershed<br />

has a silty-clay soil derived from Cody Shale.<br />

Roots penetrate this soil about 1 foot. This area is<br />

covered with Nuttall saltbrush and bottlebrush squirreltail<br />

(Sitanion hystrix). The remaining 10 percent of<br />

the watershed is comprised of high, grass-covered<br />

plateaus and of bottomlands covered with greasewood<br />

(Sarcobatus vermiculat1ts). Average annual precipitation<br />

is estimated to be about 10 inches (N.J. King, oral<br />

commun., 1969). · Runoff occurs from snowmelt and<br />

rains in the spring, and from occasional torrential summer<br />

storms (Peterson, 1961). Additional hydrologic<br />

information, including a 16 ... year record of sediment<br />

yield through July 1968, was obtained from King<br />

(1959) and from N.J. King and G. C. Lusby (written<br />

commun., 1969).<br />

RE,SULTS AND DISCUSSION<br />

Figure 2 shows the relationship of estimated sediment<br />

yields obtained with the PSIAC method to<br />

measured sediment yields for three sets of watersheds.<br />

In all three sets, with the exception of the low-sediment-yielding<br />

watersheds in Wyoming, the estimates<br />

tend to be lower than reservoir values, as most of the<br />

points lie above the 1 :1 lines in figure 2. Also, the mean<br />

sediment-yield estimate for all sites is 1.4 acre-feet<br />

per square mile, and the mean for the reservoir records<br />

is 1.73.<br />

The tendency for the estimated sediment yields to<br />

be lower ·than reservoir records is attributed to the<br />

author's bias in rating some of the factors lower than<br />

they should have been, but no factor was consciously<br />

rated consistently low. After the watersheds had been<br />

rated, it was apparent that the channel erosion and<br />

sediment transport factor had not been rated high<br />

enough for some of the steeper watersheds having raw<br />

gullies. The ratings were accordingly increased for<br />

some of the Badger Wash and New Mexico watersheds,<br />

resulting in smaller differences between the estimated<br />

and measured sediment yields. The correlation of measured<br />

runoff with values for the runoff factor in the<br />

method was rather poor; the coefficient of correlation<br />

(1·) was 0.34. No objective means of adjusting values<br />

for the runoff factor was found.<br />

The correlation of watershed area with the difference<br />

between reservoir measurements and the estimates was<br />

very poor ( r = 0.13). Apparently, on very small watersheds,<br />

the PSIAC method sufficiently accounts for expected<br />

larger sediment yields per unit area caused by<br />

greater average slope, intense storms covering the<br />

whole watershed, and small transit losses. This indicates<br />

that the method may have application in the de-<br />

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ESTIMATED SEDIMENT YIELD, IN<br />

ACRE-FEET PER SQUARE MILE<br />

;-<<br />

FIGURE 2.-Graphs showing reLationship of estimated<br />

sediment yields to measured sediment<br />

yi,elds, determined by the Pacific Southwest<br />

Inter-Agency Committee method, for reservoirs<br />

in three sets of watersheds: A, Badger Wash,<br />

Colo.; B, New Mexico; C, Wyoming. All correlation<br />

coefficients ( 1·) are significant at the 1-<br />

percent level. The solid lines are lines of<br />

equality where the estimated sediment yields<br />

equal the measured sediment yields. The<br />

dashed lines are regression lines fitted to the<br />

points.<br />

sign of structures for small watersheds and in proposals<br />

for land treatment, in addition to its use for 1naking<br />

broad sediment classifications of larger areas.<br />

In applying this method, good records from gaged<br />

areas, where available, should be used to check the estimates.<br />

If the estimates and records do not reasonably<br />

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