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GENERAL33122
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Last modified
8/24/2016 7:55:16 PM
Creation date
11/23/2007 7:31:41 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1981033
IBM Index Class Name
General Documents
Doc Date
3/31/1982
Doc Name
PROPOSED DECISION and FINDINGS OF COMPLIANCE
From
Mine No. 1, No. 2 & No. 3
Permit Index Doc Type
FINDINGS
Media Type
D
Archive
No
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-43- <br />Water Balance <br />A water balance for the North Fork of the Gunnison River has been performed for the <br />watershed whose boundaries are illustrated in Figure I. The boundaries can be <br />effectively divided into two sections; namely, North of the North Fork of the <br />Gunnison River and South of the North Fork of the Gunnison River. Table 5 identifies <br />how much area exists in each section, along with approximate average elevations. <br />In order to perform a mss balance on this area, it is necessary to determine how <br />much precipitation occurs annually. One technique that can be used is to utilize <br />existing precipitation data. However, only two precipitation stations exist for the <br />watershed; one at Paonia and one at Wilcox Ranch. Since these are .located near the <br />North Fork of the Gunnison River, it was felt that precipitation values obtained <br />would not adequately represent the total watershed. Therefore, isohyetal lines were <br />used to determine average precipitation and total amount of water that falls on the <br />watershed. Figure 4 represents mean annual precipitation and Figure 5 illustrates <br />May to September precipitation of the years 1931 to 1960. All values were obtained <br />from maps drawn by the U.S. Weather Bureau. Table 6 summarizes precipitation data <br />for both the North and South sections of the watershed. <br />Outflow from the system will occur by surface flows, ground water flows, evapo- <br />transpiration, and diversions. Of these outflow components, evapotranspiration <br />is the most difficult to quantify. Various techniques exist to determine how much <br />evapotranspiration occurs. For this study, the technique proposed by Ramon (1961) <br />was utilized to determine a value for potential evapotranspiration (PET). The <br />advantage of utilizing Hamon's equation is that the value determined for PET <br />will represent a net value for all vegetative cover. This is in contrast to the <br />values obtained by other methods, such as the Blaney-Criddle method or the <br />Jensen-Raise method, where the values obtained for PET represent specific crops. <br />Table 6 illustrates a PET comparison for the area around Paonia, Colorado. It <br />was assumed for the Blaney-Criddle method that the entire area consisted of <br />deciduous orchards. In reality, there are many acres around Paonia that grow other <br />crops. As a result, there will be a difference between the total amount of water <br />required for PET as predicted by the Blaney-Criddle method when compared to that <br />calculated by the Ramon method. It can be concluded that utilization of the Ramon <br />technique is its ability to predict the amount of water lost by sublimation. The <br />U.S. Army Corps of Engineers (1960) found that for the middle latitudes, in the winter <br />and early spring before snowmelt runoff begins, sublimation loss from the snow <br />surface cover can be assumed, for hydrologic computation purposes, to be about ~ <br />inch of water equivalent per month. Table 6 illustrates that the loss of water <br />during winter months, as predicted by the Ramon equation, is approximately ~ inch <br />per month. Finally, the Ramon equation predicts PET for native vegetation when <br />the temperature is greater than 32.0°F. This is in contrast to other techniques, <br />which often require a minimum temperature greater than 40°F before accurate <br />results can be obtained. <br />Assuming adiabatic conditions exist so that for every 1,000 feet increase in <br />elevation, there is a decrease of 5.4oF in temperature, the values of PET for <br />the watershed were determined as illvstrated in Table 7. <br />
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