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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>.

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