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<br />The alluvial aquifer in the study area is hydrau- <br />lically connected to the Arkansas River. Accordingly, <br />the aquifer and the river can exchange water; if the <br />water-surface elevation in the river i,; higher than the <br />water-table surface in the surrounding aquifer, then the <br />river provides recharge to the aquifer and vice versa. <br />ln addition, the aquifer also can be recharged as a <br />result of modifications to the system made to accom- <br />modate irrigation procedures such as application of <br />water derived from surface-water diversions or from <br />ground water, or both. The aquifer also may discharge <br />water to local irrigation and water-supply wells. <br /> <br />Surface-Water Conveyances <br /> <br />There are two principal surface-water convey- <br />ances in the study area (fig. 1): the Fort Lyon Canal <br />and the Arkansas River. Records of discharge for the <br />fort Lyon Canal, that are from tbe gllging station <br />located downstream from the canal head gate were <br />obtained from the Colorado Division of Water <br />Resources. Records of dbcharge for the Arkansas <br />River at La Junta, a streamflow-gaging station that is <br />located at La Junta and is downstream from the diver- <br />sion at the headgate for the Fort Lyon Canal. are stored <br />in a USGS data base known as the Automated Data <br />Processing System lADAPS). <br />There are two facts about the Fort Lyon Canal <br />that need to be considered. First, the canal is unlined; <br />that is, the bottom and banks consist of native mate- <br />rials, and, as a consequence there are conveyance <br />losses (in this sense the Fort Lyon Canal provides <br />recharge to the local aquifer). In a [989 to 1990 study, <br />Dash ( 1995) estimated that losses could be as high as <br />about 15 acre-feet per day per canal mile, <br />Second, the Fort Lyon Canal gaging station is <br />located downstream from two structures that are some- <br />times used to divert water li'om the canal for mainte- <br />nance activities related to suspended sediment loads in <br />tbe canal. As a result. the gaging station does not <br />record wateT diverted through these structures. <br />Also, beginning 1975, about the middle of the <br />period being studied. Pueblo Reservoir began to <br />operate (Abbott, 1 985). Reservoir operations most <br />pertinent to the study described in this report are the <br />distribution of water stored in the reservoir for use at a <br />later time (winter water) and the distribution of water <br />available from transmountain diversion projects <br />(project water). <br /> <br />The discharge record for the Fort Lyon CanalIS <br />shown in figure 5 and table 4. Figure 5 includes the <br />annual total hydrograph, a smoothed curve of the <br />annual total hydrograph, and a line indicating the <br />long-term mean. A smoothed curve indicates general <br />patterns and is prepared using a technique called <br />locally weighted scatterplot smoothing (Cleveland and <br />others, (979), a cDlllputationally intensive technique <br />that is comparable to a moving average. Figure 5 indi- <br />cates that, generally, flow in the canal was greater than <br />the long-term mean from 1980 through 1989 during <br />the 1980's. This period includes one year of relatively <br />low flow, 1981, and also includes the highest annual <br />total flow for the period of record, 1985 (fig. 5). After <br />1989, figure 5 indicates that, generally. diversions to <br />the canal were less than the long-term mean, although <br />flow was greater than the long-tenn mean in 1996 and <br />1997 and the 1997 flow was almost as higb as the 1985 <br />diversion. The mean-daily hydrograph (fig. 5) sbows <br />typical seasonal variation of flow for tbe period <br />studied and indicates that flow is highest in June. <br />The record for flow in the Fort Lyon Canal, as <br />well as flow in tbe Arkansas River, indicates a change <br />during the late 1970's. Accordingly, flow-duration <br />,malyses were prepared to describe differences in flc>w <br />characteristics for two periods, 1960 to 1980 and 1981 <br />to 1997, The results for this study (table 5) list a <br />percentage of time. from the period of record being <br />analyzed, that the corresponding rate of flow was <br />exceeded. <br />The flow-duration statistics in table 5 indicatt <br />that there was flow in the Fort Lyon Canal more often <br />during the first period than the second. For instance, <br />there were very low flows (less than] cubic foot per <br />second) in the canal for only I to 3 percent of the first <br />period, whereas there were very low flows in tbe canal <br />for 10 to 15 percent of the second period. Perhaps <br />more importalllly, the flow-duration statistics indicate <br />tbat, due to large flows during the 1980's, flow in the <br />canal was greater, usually by a factor of I j to 2, than <br />in the first period. For example. diversions in the callal <br />were greater than about 345 cubic feet per second for <br />50 percent of the second period; in the first period the <br />50 percent exceedance flow was about 213 cubic fe'~t <br />per second. <br />The discharge record for the Arkansas River ,1t <br />La Junta is shown in figure 6. The annual total and <br />particularly the mean-daily hydrographs are generally <br />similar to the hydrographs for the Fort Lyon Canal <br />(fig. 5). The smoothed curve for the annual total flow <br /> <br />16 Analysis ot HydrologiC Factors. That Affect Ground~Water l.evels in the Arkansas River AUuviat Aquifer Near La Junta, ColoradO, <br />1959-99 <br />