Dames & Moore, 1999 - USDA Forest Service
Dames & Moore, 1999 - USDA Forest Service Dames & Moore, 1999 - USDA Forest Service
stable slope while factors of safety at or below 1.0 indicate impending failure of the slope. Slopes with factors of safety between 1.0 and 1.2 are considered marginally stable. This seismic event has an estimated return period of approximately 40 years at the Site location. Graphical representations of the analyses for seismic conditions, including site stratigraphy, groundwater elevation and topography, are presented on Figures 4.2-19 and 4.2-20. Only results for the smaller 40-year return period seismic event are shown on the figures. As noted on Figures 4.2-17 through 4.2-20, the slope stability analysis included modeling a "cemented layer" on the surface of the slopes. It was not possible to complete subsurface explorations on the slopes of the tailings piles to characterize the thickness of the cemented layer due to the steepness of the slopes. However, based on boring and test pit data collected from the tailings piles, including test pits excavated by Dames & Moore in 1997 near the top and base of tailings piles 1 through 3 (DMTPI-2 through DMTP3-4, shown on Figure 4.2-6b), it appears that the thickness of the "cemented layer" ranges from several inches to approximately 10 feet. The slope stability analysis utilized the lower end of the range (approximately 3 feet). Since the slope stability failure circles noted on Figures 4.2-17 through 4.2-20 extend below the maximum observed thickness of the cemented layer, the effect of cementation is thought to be minimal. The analyses did not include scenarios of either no cemented zone or a 10-foot-thick cemented zone. In addition, groundwater levels were assumed to be near the base of the tailings piles and not perched higher within the tailings. Given the various observations from the RI reconnaissance, boring logs, groundwater monitoring well data, test pits and slope performance over the years, the scenario utilized in the analyses appears to be reasonable. As noted for the liquefaction analyses, there is some level of uncertainty associated with the findings of the slope stability analyses due to uncertainties related to the engineering properties of the tailings and native materials, groundwater levels, the presencelabsence and degree of cementation, and the modeling utilized. The observed long-term performance of the slopes suggests they are actually more stable than indicated by the results of the static and seismic analyses. The tailings pile slopes are relatively steep, but have not experienced a reported failure since a flood which occurred in 1948 and appeared to have been a 50-year event (Crates, 1966); the 1948 storm event resulted in the eroding of the toe of the northwest portion of tailings pile 2 and the delivery of tailings to railroad Creek. The slopes have held the relatively steep angles since the 1948 event, but are steeper than the angle of repose as determined by the angle of internal friction (37 degrees) resulting from laboratory testing completed by Hart Crowser. In addition, the Site apparently experienced a relatively significant seismic event in 1990, which did not result in slope failure. Therefore, it is our opinion that the soils have been appropriately and possibly conservatively modeled during the slope stability analyses. Possible measures to mitigate the mass movement potential will be addressed in the FS document. Any erosion at the toe of the slope (such as Railroad Creek cutting into the slope) will reduce the factors of safety described above. Erosion is discussed further in Section 4.2.4.3 below. Based on the observed angular nature of the waste rock piles, it is estimated that potential for slope failure is relatively low. However, isolated, shallow failures have the potential to occur on the steepest slopes. G:\WPDATA\O05WPORTSWOLDEN-2UUW-O-ODOC 17693-005-019Uuly 19. 1999;4:51 PM;DRAFT FINAL RI REPORT '
Tailings pile 3 is situated near the base of an avalanche chute. An avalanche reportedly ter'minated near the southern edge of the pile in 1996 (persdnal communication with Keith Anderson, USFS, 1997). The potential exists for an avalanche to deliver avalanche debris to the southern margin of the tailings pile. 4.2.4.3 Erosion Potential Summary of Historical Findings Erosion is the breakdown of soils and bedrock by natural processes including water, wind, and glaciation. Of these processes, water-related erosion during storm events has the most potential for adverse impact. Fine-grained soil is also susceptible to wind erosion. The susceptibility of any material to erosion is dependent upon: (1) chemical and physical characteristics, (2) topography, (3) the amount and intensky of precipitation and surface water, and 4) the type and density of vegetative ground cover, if present. The tailings material was found in the ORB 1975 report to be "highly susceptible to erosion by wind and water" prior to the placement of the gravel surfacing and grass mats. The report noted that windblown deposits were measured 500 feet downwind of the piles in amounts over 3,000 pounds per acre. Based on the reported average dry unit density of 92 pcf, this would equal approximately 0.009 inches of tailings material at that location. The report also concluded that a wind velocity of 30 cmlsec was needed to start eroding the tailings material; the assumptions associated with this estimate were not provided. RI Findings Railroad Creek flows eastward for approximately 3,900 feet directly adjacent to the three tailings piles. The tailings piles lie from 30 to 120 feet above the main channel on the south side of the creek. A field reconnaissance along the creek and slopes of the tailings was conducted. During the reconnaissance, the 3,900 feet of creek reach along the tailings slopes was classified into 18 different slope reaches with apparent similar erosion processes and erosion potential (e.g., slope angle, setback fiom creek, amount of vegetation, relationship to high water, etc.). Schematic cross-sections for each slope reach are presented in Appendix F. The criteria for grading and ranking the slopes in terms of erosion potential are presented in Tables 4.2-2 and 4.2-2% respectively. Physical characteristics for each slope reach are summarized in Table 4.2-3. The logs of the test trench excavations are presented in Appendix C. In general, the trench excavations indicate that the undisturbed tailings soils are predominantly laminated fine-grained sands that grade to silts and have pockets or lenses of clay; however, due to an uneven decrease in oxidation fiom the slope inward and from the top down, the soils appear laterally and vertically heterogeneous in color and the degree of cementation. For example, there are abrupt and irregular contacts of well oxidized hard, dry, cemented, medium-orange fine-grained sands in contact with loose, moist to dry, non-cemented, medium- to dark-gray fine-grained sands. In some cases, the upper 2 to 4 ft of tailings soils are softer, looser and more uniform in color and have no internal structure (i.e., the sands and silts are well mixed), and appear to have been remolded. The remolding most likely took place when the slopes were reconfigured during the USFS reclamation activities. 'soft, loose remolded soil also occurs on the slbpes and at the base forming a thick talus in places. Wood pieces were also observed in most trenches, and in a few places, cut timber logs were found buried in a vertical position. G:\WPDATA\OOJWPORTSWOLDEN-ZW-O.DOC 17693-005-019Uuly 19, 1999:4:Jl PM:DRAFT FINAL RI REPORT
- Page 114 and 115: SOURCE: USGS Topographic Map, State
- Page 116 and 117: - Figure 3.0-3 DAMES & MOORE HOLDEN
- Page 118 and 119: Figure 3.1-2 DAMES & MOORE ! RI SOI
- Page 121 and 122: Fill (2) Vent (1) SOURCE: Base map
- Page 123: SOURCE: Base map information from U
- Page 126 and 127: SOURCE: WIteffi et a/., 1992 USGS C
- Page 129 and 130: DAMES & MOORE Figure 3.4-2 FLOCCULE
- Page 133 and 134: i I i .4 i ,i i i\ i '.\ i \ \ i I
- Page 135 and 136: 4.1.2 Site Surface Features Referri
- Page 137 and 138: Hydroelectric Plant Electrical powe
- Page 139 and 140: Water seepage emanates, in the spri
- Page 141 and 142: '7 ~t the Site, approximately mid-w
- Page 143 and 144: system delineated by ditches and re
- Page 145 and 146: Section I-I' and shows the six tunn
- Page 147 and 148: The uppermost stopes within the min
- Page 149 and 150: make up the earth's surface. The st
- Page 151 and 152: silver, and included 34,000 tons of
- Page 153 and 154: strength was determined by Hart Cro
- Page 155 and 156: gravels are variable in thickness a
- Page 157 and 158: wetlands and adjacent to Railroad C
- Page 159 and 160: Several faults have been mapped in
- Page 161 and 162: the coefficient of Friction. Geomor
- Page 163: The groundwater levels used for the
- Page 167 and 168: vertical extent of the underground
- Page 169 and 170: from the roof, then evaluating the
- Page 171 and 172: 4.2.8 Potential Borrow Source Areas
- Page 173 and 174: for good quality riprap would neces
- Page 175 and 176: May and June, which coincide with t
- Page 177 and 178: Rating Calculations Referring to Ta
- Page 179 and 180: with little or no braiding. Upstrea
- Page 181 and 182: Discharge in Railroad Creek was mon
- Page 183 and 184: model predicted a 100-year flood at
- Page 185 and 186: The data logger, or transducer, was
- Page 187 and 188: submerged at high water levels. Flo
- Page 189 and 190: this, it is possible that the snow
- Page 191 and 192: 4.3.5 Basin Average Climatic Water
- Page 193 and 194: surface erosional features provide
- Page 195 and 196: * The D50 equation is obtained from
- Page 197 and 198: effect of a 0.05-foot stage increas
- Page 199 and 200: discussed in' Section 6.8.2 of this
- Page 201 and 202: Observations During Aquatic snorkel
- Page 203 and 204: covers limited portions of the Site
- Page 205 and 206: Bedrock Bedrock underlies the entir
- Page 207 and 208: high as 0.1 to 0.2 feet per foot (F
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Tailings pile 3 is situated near the base of an avalanche chute. An avalanche reportedly ter'minated near the<br />
southern edge of the pile in 1996 (persdnal communication with Keith Anderson, USFS, 1997). The<br />
potential exists for an avalanche to deliver avalanche debris to the southern margin of the tailings pile.<br />
4.2.4.3 Erosion Potential<br />
Summary of Historical Findings<br />
Erosion is the breakdown of soils and bedrock by natural processes including water, wind, and glaciation.<br />
Of these processes, water-related erosion during storm events has the most potential for adverse impact.<br />
Fine-grained soil is also susceptible to wind erosion. The susceptibility of any material to erosion is<br />
dependent upon: (1) chemical and physical characteristics, (2) topography, (3) the amount and intensky of<br />
precipitation and surface water, and 4) the type and density of vegetative ground cover, if present.<br />
The tailings material was found in the ORB 1975 report to be "highly susceptible to erosion by wind and<br />
water" prior to the placement of the gravel surfacing and grass mats. The report noted that windblown<br />
deposits were measured 500 feet downwind of the piles in amounts over 3,000 pounds per acre. Based on<br />
the reported average dry unit density of 92 pcf, this would equal approximately 0.009 inches of tailings<br />
material at that location. The report also concluded that a wind velocity of 30 cmlsec was needed to start<br />
eroding the tailings material; the assumptions associated with this estimate were not provided.<br />
RI Findings<br />
Railroad Creek flows eastward for approximately 3,900 feet directly adjacent to the three tailings piles. The<br />
tailings piles lie from 30 to 120 feet above the main channel on the south side of the creek. A field<br />
reconnaissance along the creek and slopes of the tailings was conducted. During the reconnaissance, the<br />
3,900 feet of creek reach along the tailings slopes was classified into 18 different slope reaches with<br />
apparent similar erosion processes and erosion potential (e.g., slope angle, setback fiom creek, amount of<br />
vegetation, relationship to high water, etc.). Schematic cross-sections for each slope reach are presented in<br />
Appendix F. The criteria for grading and ranking the slopes in terms of erosion potential are presented in<br />
Tables 4.2-2 and 4.2-2% respectively. Physical characteristics for each slope reach are summarized in<br />
Table 4.2-3.<br />
The logs of the test trench excavations are presented in Appendix C. In general, the trench excavations<br />
indicate that the undisturbed tailings soils are predominantly laminated fine-grained sands that grade to silts<br />
and have pockets or lenses of clay; however, due to an uneven decrease in oxidation fiom the slope inward<br />
and from the top down, the soils appear laterally and vertically heterogeneous in color and the degree of<br />
cementation. For example, there are abrupt and irregular contacts of well oxidized hard, dry, cemented,<br />
medium-orange fine-grained sands in contact with loose, moist to dry, non-cemented, medium- to dark-gray<br />
fine-grained sands. In some cases, the upper 2 to 4 ft of tailings soils are softer, looser and more uniform in<br />
color and have no internal structure (i.e., the sands and silts are well mixed), and appear to have been<br />
remolded. The remolding most likely took place when the slopes were reconfigured during the USFS<br />
reclamation activities. 'soft, loose remolded soil also occurs on the slbpes and at the base forming a thick<br />
talus in places. Wood pieces were also observed in most trenches, and in a few places, cut timber logs were<br />
found buried in a vertical position.<br />
G:\WPDATA\OOJWPORTSWOLDEN-ZW-O.DOC<br />
17693-005-019Uuly 19, <strong>1999</strong>:4:Jl PM:DRAFT FINAL RI REPORT