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<br />surface-water applications for irrigation are made <br />through diversions out of the Fort Lyon Canal into <br />local laterals that deliver water to fields. Usually, the <br />water is used to flood the fields. In this respect, the <br />Fort Lyon Canal represents a source of recharge to the <br />local aquifer. <br />Goff and others (1998) computed annual <br />surface-water applications using an algorithm that was <br />based on the amount of water in the canal and the ratio <br />of irrigation-program participants in the study area to <br />the total number of participants who are supplied by <br />the canal. The results of their estimates are listed in <br />table 4. Surface-water applications were greater than <br />the long-term mean during most of the 1980's, similar <br />to flow in the Fort Lyon Canal, which generally was <br />high during that decade. After the 1980's, surface- <br />water applications decreased and returned to levels <br />slightly higher than those preceding the 1980's. <br /> <br />Ground-Water Withdrawals <br /> <br />When necessary, generally when water is not <br />available from the Fort Lyon Canal, ground water is <br />routinely withdrawn from the local aquifer for irriga- <br />tion purposes to supplement irrigation made with <br />surface-water diversions. Ground water also is with- <br />drawn for public water supply. These withdrawals <br />represent discharge from the aquifer. Irrigation wells <br />are distributed throughout the study area in a relatively <br />uniform fashion; however water-supply wells, oper- <br />ated by the city of La Junta are clustered in an area of <br />La Junta on the north side of the Arkansas River. <br />Ground water is withdrawn for irrigation throughout <br />the study area and is usually used to flood fields, <br />although some alternative methods, such as spray and <br />drip irrigation, are used. The records available for <br />analysis in this study are from a previous study (Goff <br />and others, 1998) and are summarized in table 4. They <br />are annual records and are based on reported with- <br />drawals from the city of La Junta and on a power <br />conversion method (Boyle Engineering Corp., 1990) <br />for irrigation wells that estimates the amount of water <br />withdrawn at individual wells based on electric power <br />meter readings. <br />The Colorado Division of Water Resources has <br />recently begun to maintain records of withdrawals <br />made by irrigation wells. The records are for indi- <br />vidual wells and have more detail than is available <br />from the historical records. These contemporary <br /> <br />records should be very useful, in the future, for charac- <br />terizing the amount of ground water withdrawn for <br />irrigation. <br />The records from Goff and others (1998) indi- <br />cate that ground-water withdrawals generally have <br />decreased in the study area (table 4). In 1972 and from <br />1974 through 1978, withdrawals were greater than the <br />long-term mean and increased steadily to a high for <br />the period of record. After a peak in mid 1976, <br />decreases began and continued through about 1987, <br />after which ground-water withdrawals became rela- <br />tively steady at a level less than the long-term mean. <br />The records indicate that ground-water withdrawals at <br />the end of the period of record were much less than the <br />withdrawals made in the late 1970's and early 1980's. <br />The records also indicate that although ground-water <br />withdrawals in the study area sometimes have a nearly <br />one-to-one inverse relation to surface-water appIica- <br />tions, such as in the late 1970's and early 1980's, the <br />relation is not necessarily constant, such as in the <br />period after the mid- 1980's when surface-water appli- <br />cations are nearly constant and ground-water with- <br />drawals tend to increase. <br /> <br />Channel Processes <br /> <br />As stated previously, the Arkansas River and the <br />surrounding alluvial aquifer can exchange water. <br />When the river is recharging the aquifer, the amount of <br />recharge increases as the level of the river increases. In <br />the short term, increases in river level, or stage, are <br />related to changes in rates of flow. For instance, flow <br />typically increases when there are widespread rains. In <br />the long term, however, the level of the river may <br />change due to increases in the elevation of the river <br />bed. Long-term changes in the river-bed elevation <br />affect ground-water discharge, or drainage, to the <br />river. In general, ground water at elevations lower than <br />the river bed will not drain from the system and the <br />river bed forms a base level for ground water. <br />Walls and Lunsford (1992) documented a <br />general increase in the elevation of the river bed for <br />the Arkansas River at La Junta by evaluating the eleva- <br />tion of the point of zero flow, which is determined <br />routinely as a part of maintaining streamflow records. <br />In this study, a similar method was used to evaluate <br />changes in river-bed elevation. <br />The method used in this study, sometimes <br />referred to as the "specific-stage method" <br /> <br />HYDROLOGIC FACTORS THAT AFFECT GROUND.WATER LEVEL.S 21 <br />