Ground-Water Hydrology of the Upper Klamath Basin, Oregon and ...
Ground-Water Hydrology of the Upper Klamath Basin, Oregon and ...
Ground-Water Hydrology of the Upper Klamath Basin, Oregon and ...
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<strong>Ground</strong>-<strong>Water</strong> <strong>Hydrology</strong> 59<br />
Long-term water-level trends in northwest Langell Valley<br />
<strong>and</strong> east <strong>of</strong> Lorella indicate that pumping stresses in those<br />
areas are periodically greater than average (for <strong>the</strong> area),<br />
probably resulting from <strong>the</strong> occasional use <strong>of</strong> supplemental<br />
ground-water rights. The water level in <strong>the</strong> observation well<br />
in northwest Langell Valley (39S/11E-26ABD) apparently<br />
responded to increased pumping during <strong>the</strong> 1970s, again in <strong>the</strong><br />
early 1990s, <strong>and</strong> again starting in 2001 (fig. 36). The groundwater<br />
flow system nearly recovered after each <strong>of</strong> <strong>the</strong> earlier<br />
cycles. In 2005, <strong>the</strong> water level was about 13 ft below <strong>the</strong> level<br />
measured during 1998, <strong>the</strong> most recent wet period. A trend<br />
similar to that observed in <strong>the</strong> Langell Valley well, but with<br />
a smaller amplitude <strong>of</strong> fluctuation, is seen in <strong>the</strong> long-term<br />
record at well 39S/12E-35ADD, just east <strong>of</strong> Lorella (fig. 36).<br />
The 2005 water level in <strong>the</strong> Lorella well was only about 4 ft<br />
below <strong>the</strong> 1998 measurement. Recharge from canal leakage in<br />
<strong>the</strong> area may also be influencing <strong>the</strong> water-level trend in <strong>the</strong><br />
Lorella well (Grondin, 2004).<br />
Recent pumping stresses in <strong>the</strong> <strong>Klamath</strong> Valley area<br />
are reflected in water levels measured in observation well<br />
41S/09E-12AAB (fig. 37). With <strong>the</strong> exception <strong>of</strong> a sharp<br />
decline in 1970, <strong>the</strong> water-level trend in <strong>the</strong> well appears to<br />
have been in dynamic equilibrium until 2001. The increased<br />
pumping stresses combined with drought contributed to a<br />
water-level decline <strong>of</strong> about 12 ft between 2001 <strong>and</strong> 2004.<br />
Fluctuations in Hydraulic Head in Response to<br />
Recent Increases in <strong>Ground</strong>-<strong>Water</strong> Pumping<br />
Prior to 2001, <strong>the</strong> ground-water system in most <strong>of</strong> <strong>the</strong><br />
upper <strong>Klamath</strong> <strong>Basin</strong> was in a state <strong>of</strong> dynamic equilibrium,<br />
under which water levels rose <strong>and</strong> fell in response to climate<br />
cycles <strong>and</strong> seasonal pumping, but generally without chronic<br />
long-term declines. (<strong>Water</strong> levels in some wells near <strong>the</strong> town<br />
<strong>of</strong> Sprague River [fig. 33] are an exception.) Historically,<br />
water levels declined for several years during droughts, but,<br />
with local exceptions, water levels eventually rose to (or<br />
nearly to) predrought levels during subsequent multiyear<br />
wet periods. Wells generally have been drilled deep enough<br />
<strong>and</strong> pumps set low enough to accommodate <strong>the</strong>se historical<br />
water-level fluctuations. Pumping in <strong>the</strong> upper <strong>Klamath</strong> <strong>Basin</strong><br />
increased an estimated 50 percent starting in 2001 in response<br />
to changes in water management <strong>and</strong> a prolonged drought. The<br />
ground-water system has responded to <strong>the</strong> increased pumping<br />
with water levels showing acute, seasonal, <strong>and</strong> long-term<br />
effects.<br />
Acute effects occur close to pumping wells, generally<br />
within hundreds to thous<strong>and</strong>s <strong>of</strong> feet. These effects typically<br />
are <strong>the</strong> result <strong>of</strong> <strong>the</strong> cone <strong>of</strong> depression <strong>of</strong> <strong>the</strong> pumping<br />
well spreading to neighboring wells, resulting in a decline<br />
in <strong>the</strong> static water levels, sometimes referred to as “well<br />
interference.” These effects typically have a rapid onset <strong>and</strong><br />
dissipate relatively soon after pumping ends.<br />
0<br />
10<br />
39S/11E-26ABD<br />
20<br />
30<br />
DEPTH TO WATER, IN FEET<br />
40<br />
50<br />
30<br />
40<br />
50<br />
60<br />
70<br />
80<br />
1950<br />
39S/12E-35ADD<br />
1955<br />
1960<br />
1965<br />
1970<br />
1975<br />
1980<br />
1985<br />
1990<br />
1995<br />
2000<br />
2005<br />
Figure 36.<br />
<strong>Water</strong>-level fluctuations in wells 39S/11E-26ABD <strong>and</strong> 39S/12E-35ADD in <strong>the</strong> western Langell Valley, <strong>Oregon</strong>.