D--048966 - CALFED Bay-Delta Program - State of California
D--048966 - CALFED Bay-Delta Program - State of California
D--048966 - CALFED Bay-Delta Program - State of California
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875<br />
Hydrology and Water Resources<br />
overland flow, predominance <strong>of</strong> subsurface flow, and rela- a portion <strong>of</strong> a slope fails all at once. Movement may be catatively<br />
continuous vegetation coven The sources and pathways strophic in seconds or progressive over years. Mass wasting<br />
<strong>of</strong> sediments supplied to stream channels are not completely may be important in providing a material supply to channels<br />
understood. The channel system itself is an obvious candi- slowly through soil creep or suddenly when a debris flow<br />
date as a source for most <strong>of</strong> the sediment (King 1993). During reaches a stream, but it is not regarded as a major erosive<br />
persistent rainfall and peak snowmelt, the network <strong>of</strong> very agent in most <strong>of</strong> the Sierra Nevada (Seidelman et al. 1986).<br />
small channels becomes rather extensive, mobilizing sediment Mass movement typically occurs when most <strong>of</strong> the pores in<br />
from a large fraction <strong>of</strong> a watershed. Such sediment probably the material become filled with water. The positive pressure<br />
does not move very far but may be made available for trans- <strong>of</strong> the pore water and its added mass may exceed the strength<br />
port by a high-magnitude run<strong>of</strong>f event. The sequence <strong>of</strong> events <strong>of</strong> the material, and failure <strong>of</strong> part <strong>of</strong> the slope may occur.<br />
<strong>of</strong> different magnitudes can determine the net sediment trans- Unusually high rates <strong>of</strong> water input to previously wet soils<br />
port over long time periods (Beven 1981). In the Sierra Ne- can lead to large numbers <strong>of</strong> landslides in the Sierra Nevada<br />
vada, the greatest potential for overland flow to occur appears (De Graft et al. 1984). Disturbance <strong>of</strong> slopes accelerates the<br />
to be below the snow zone in woodland-grassland communi- natural occurrence <strong>of</strong> landslides (Sidle et al. 1985). Excaties<br />
between 300 and 900 m (1,000 and 3,000 ft) (Helley 1966). vations across slopes for roads intercept water flowing<br />
The maximum rates <strong>of</strong> sediment production have been ob- downslope through the soil and increase pore water pressure<br />
served in this same altitude range (Janda 1966). The wood- at the exposed seepage face. In granitic portions <strong>of</strong> the Sierra<br />
land zone also was the primary sediment source in part <strong>of</strong> Nevada, ground-water flow is <strong>of</strong>ten at a maximum at the inthe<br />
American River Basin with annual erosion <strong>of</strong> about 150 terface between the porous coarse-grained soils and underlym3/km<br />
2 (0.3 AF/mi 2) (Soil Conservation Service 1979). ing relatively impermeable bedrock (De Graft 1985). Exposure<br />
<strong>of</strong> this layer can bring large quantities <strong>of</strong> water to the surface<br />
Accelerated Erosion<br />
(Seidelman et al. I986). Such excavations also reduce the me-<br />
Human activities <strong>of</strong>ten disrupt the natural geomorphic prochanical<br />
support for adjacent parts <strong>of</strong> the slope. Tree roots are<br />
<strong>of</strong>ten important in maintaining the integrity <strong>of</strong> a slope. Minicesses<br />
and accelerate erosion or destabilize hill slopes. Mod- mum strength occurs about ten years after fire or timber<br />
eling erosion in the Camp and Clear Creek Basins suggests harvesting when roots from young trees have not yet cornthat<br />
disturbance, especially roads, can increase erosion many pensated for the progressive loss <strong>of</strong> old roots (Ziemer 1981).<br />
times above natural rates (McGurk et al. 1996). When soil loss Most opportunities to minimize mass wasting as a conseand<br />
sediment transport occur at unusually high rates in re- quence <strong>of</strong> road construction and forest harvesting involve<br />
sponse to some human disturbance, erosion and sedimen- commonsense approaches to avoiding accumulation <strong>of</strong> subtation<br />
become issues <strong>of</strong> concern. Accelerated soil loss is surface water on steep slopes (Sidle 1980; McCashion and Rice<br />
primarily a problem in terms <strong>of</strong> losing productivity for grow- 1983).<br />
ing vegetation (P<strong>of</strong>f 1996). Excessive sedimentation can dam- In years <strong>of</strong> high precipitation with large individual storms,<br />
age terrestrial plants and aquatic organisms. High levels <strong>of</strong> the number, extent, and size <strong>of</strong> mass movements increase well<br />
sediment deposition can also reduce the utility <strong>of</strong> facilities above those <strong>of</strong> years with modest precipitation. Landslides<br />
for water storage and diversion and hydroelectric produc- were particularly active during the wet years <strong>of</strong> 1982 and 1983.<br />
tion. At the extreme, hydraulic mining for gold on the west In both those years, springs and seeps appeared in places they<br />
slope <strong>of</strong> the Sierra’Nevada intentionally eroded entire hill- had not been noticed before, including many road cuts and<br />
sides. The resulting sedimentation in downstream river chan- fills. More than $2 million in damage occurred to roads on<br />
nels left deposits tens <strong>of</strong> meters thick. Sediment yield in the national forests in the Sierra Nevada during 1982, and addi-<br />
Yuba River was up to twenty-five times greater than natural tional damage estimated at more than $1 million occurred in<br />
rates (Gilbert 1917) and led to a legal decision effectively halt- 1983 (De Graft 1987). A landslide in the American River caning<br />
hydraulic mining. Activities that purposefully move soil,-~ yon blocked U.S. 50 for April, May, and June <strong>of</strong> 1983. Sus-<br />
such as construction <strong>of</strong> roads and structures, have the great- I<br />
tained high levels <strong>of</strong> soil moisture and ground water occurred<br />
est potential for increasing erosion. Activities that reduce veg- ! throughout the winter and spring <strong>of</strong> each year. Additional<br />
etative cover and root strength can also increase erosion rates, water input from rainfall, combined rainfall and snowmelt,<br />
Activities in and near stream channels have the greatest po- and snowmelt alone triggered the unusual number <strong>of</strong> failtential<br />
for altering sediment delivery and storage as well as ures (Bergman 1987; De Graft 1987). However, there seems to<br />
channel form. For example, destruction <strong>of</strong> riparian vegeta- be relatively little interaction between high flows and initiation<br />
can lead to massive streambank erosion, or dams can trap tion <strong>of</strong> landslides within the inner gorges <strong>of</strong> Sierra Nevada<br />
sediment from upstream while causing channel incision or streams (Seidelman et aL 1986). Landslides can also be initinarrowing<br />
downstream, ated by earthquakes (Harp et al. 1984) and summer thunder-<br />
Processes involving movement <strong>of</strong> large units <strong>of</strong> soil or rock storms (Glancy 1969). An extraordinarily intense storm<br />
rather than individual particles are collectively known as mass occurred in the headwaters <strong>of</strong> the South Fork <strong>of</strong> the Ameriwasting.<br />
Landslide activity is a typical mass failure in which can River on June 18, 1982 (Kuehn 1987). About 100 mm (4 in)<br />
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