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> 57<br />
<strong>Water</strong> levels in two observation wells near <strong>the</strong> town<br />
<strong>of</strong> Sprague River, 36S/10E-14ACC <strong>and</strong> 36S/11E-20DCA<br />
(fig. 33), have declined over 30 ft since monitoring began<br />
in <strong>the</strong> early 1960s. Leonard <strong>and</strong> Harris (1974) hypo<strong>the</strong>sized<br />
that <strong>the</strong> relatively steady, <strong>and</strong> somewhat localized, longterm<br />
decline represented a loss <strong>of</strong> hydraulic head caused<br />
by discharge from free-flowing wells. The OWRD later<br />
attributed <strong>the</strong> decline, at least in part, to some wells in <strong>the</strong><br />
area constructed in a manner that allowed ground water<br />
from a <strong>the</strong> confined basalt aquifer in <strong>the</strong> lower parts <strong>of</strong> <strong>the</strong><br />
wells to flow uphole <strong>and</strong> into sedimentary units (with lower<br />
head) in shallower parts <strong>of</strong> <strong>the</strong> well bores (<strong>Oregon</strong> <strong>Water</strong><br />
Resources Department, 1987). Borehole geophysical logging<br />
has confirmed <strong>the</strong> interaquifer leakage; however <strong>the</strong> geologic<br />
units receiving <strong>the</strong> leakage appear to be rhyolitic lavas mapped<br />
in <strong>the</strong> area by Sherrod <strong>and</strong> Pickthorn (1992) (Mark Norton,<br />
<strong>Oregon</strong> <strong>Water</strong> Resources Department, unpub. data). For<br />
example, geophysical logs for one nearby well show uphole<br />
interaquifer flow <strong>of</strong> about 200 gal/min into a unit with a<br />
relatively high natural gamma signature indicative <strong>of</strong> silicic<br />
material. The driller described <strong>the</strong> material as “broken lava<br />
rock.” <strong>Water</strong> levels in both wells have been more stable since<br />
<strong>the</strong> mid-1990s (fig. 33), likely owing to <strong>the</strong> ground-water-flow<br />
system beginning to reach a new equilibrium.<br />
<strong>Water</strong> levels in long-term observation well 46N/01E-<br />
06N01 in Butte Valley were stable from <strong>the</strong> 1950s to <strong>the</strong> mid-<br />
1970s (fig. 34). Since 1975, <strong>the</strong> water level has declined about<br />
20 ft. The trend likely reflects increased pumping stresses<br />
during times when precipitation is low, with intermittent times<br />
<strong>of</strong> partial recovery during wet years in <strong>the</strong> mid-1980s <strong>and</strong> mid-<br />
1990s.<br />
An observation well in sou<strong>the</strong>rn Poe Valley (40S/11E-<br />
11BAD) shows a series <strong>of</strong> responses to development from<br />
which it has never fully recovered (fig. 35). Most notable is<br />
<strong>the</strong> water-level decline <strong>of</strong> about 20 ft between 1985 <strong>and</strong> 1995,<br />
a recovery <strong>of</strong> less than 5 ft between 1995 <strong>and</strong> 1998, <strong>and</strong> a<br />
decline <strong>of</strong> about 12 ft since 1998. Ano<strong>the</strong>r observation well<br />
(40S/12E-30DCB) about 3 mi south-sou<strong>the</strong>ast <strong>of</strong> <strong>the</strong> Poe<br />
Valley well, in <strong>the</strong> area <strong>of</strong> <strong>the</strong> Shasta View Irrigation District,<br />
has a similar water-level trend where <strong>the</strong> records overlap from<br />
1994 to present (fig. 35). The total decline in well 40S/12E-<br />
30DCB since 1998, however, is slightly greater at about 19 ft.<br />
The similarity <strong>of</strong> <strong>the</strong> head fluctuations suggests that <strong>the</strong> effects<br />
<strong>of</strong> pumping stresses in both areas may migrate across <strong>the</strong><br />
subbasin boundary.<br />
0<br />
10<br />
36S/10E-14ACC<br />
20<br />
30<br />
40<br />
50<br />
DEPTH TO WATER, IN FEET<br />
60<br />
70<br />
80<br />
90<br />
40<br />
50<br />
60<br />
70<br />
80<br />
90<br />
100<br />
1960<br />
36S/11E-20DCA<br />
1965<br />
1970<br />
1975<br />
1980<br />
1985<br />
1990<br />
1995<br />
2000<br />
2005<br />
Figure 33.<br />
<strong>Water</strong>-level fluctuations in wells 36S/10E-14ACC <strong>and</strong> 36S/11E-20DCA in <strong>the</strong> Sprague River Valley, <strong>Oregon</strong>.