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1130 GEOENV!RONMENT 2000 <br />using good waste placement practice. Furthermore, the constant unit weight used <br />at depths in the interpreted Puente Hills profile is not consistent with the assumption <br />that waste will continue to compress with additional confining pressure, even at very <br />large confining pressures. Therefore, based upon reported initial in~place waste <br />densities for modern landfills and the waste compressibility values reported by <br />Fassett et al. (1994), the interpreted Puente Hills profile was modified to develop the <br />authors' profile shown on Figure 1. In the absence of site specific information ,the <br />authors have used this profile in engineering analysis of the seismic response of <br />modern MSW landfills. <br />MSW SHEAR STRENGTH <br />MSW shear strength values reported in the technical literature vary widely, <br />with friction angles as low as 10 degrees and as high as 53 degrees and cohesion <br />values varying from 0 to 67 kPa. Many of the lower values are directly contradicted <br />by observations of stable landfill slopes in the field. Therefore, a critical re- <br />evaluation of the available shear strength data on MSW was performed by the <br />authors. The authors used selected data from this re-evaluation, supplemented with <br />shear strength back-calculated from observations of stable waste slopes in the field, <br />to develop the assessment of MSW shear strength presented herein. <br />In performing the assessment of MSW shear strength, the authors recognized <br />that factors such as waste compressibility and strain compatibility should be <br />considered when developing strength parameters for limit equilibrium analysis. The <br />authors assessment of MSW shear strength was based primarily on shear strengths <br />back-calculated from case histories and the results of in-situ testing. With the <br />exception of one set of data from large scale tests, laboratory test data on MSW <br />shear strength was not used. The excluded laboratory data was not considered <br />reliable due to either the use of processed waste in the testing program or the small <br />size of the MSW samples relative to the inhomogeneity of MSW landfills. Field and <br />laboratory test data considered reliable and used in the re-evaluation of MSW shear <br />strength are summarized in Table 1. <br />TABLE 1 DATA USED IN TilE MSW SHEAR STRENGTH REEVALUATION - <br />REFERENCE DATA TYPE RESULTS COMMENTS <br />Pagono and Back calculation ¢ = 22°, c = 29kPa No data on waste types or test <br />Rimoldi from plate procedures are provided. <br />(1987) bearing tests. <br />Landva and Clark Laboratory direct ¢ = 240, c = 22 kPa Normal stresses up to 480 kPa. <br />(1990) sh= tests on to Lower strength not used in Fig. <br />MSW. ¢ = 390, c = 19 kPa 2, corresponds to shredded waste. <br />Richardson and Large direct tP = 18° to 43° Normal stresses range from 14 to <br />Reynolds (1991) shear tests and 38 kPa. Unit weight of waste <br />performed in situ c = 10 kPa and cover estimated as 15 kN/m3 • <br />MSW PROPERTIES 1131 <br />Pagotto and Rimoldi (1987) reported the results of plate-bearing tests <br />performed at an "urban waste" landfill in Italy. No details are given on waste <br />properties, test methods, or test interpretation. Considering the limitations of plate- <br />bearing tests, these results must correspond to very low normal stresses in the waste. <br />Landva and Clark (1990) presented the results of direct shear tests on MSW <br />materials conducted in a 434 mm by 287 nun direct shear box at normal stresses up <br />to 480 kPa. Results reported for fresh shredded refuse containing a large amount <br />of plastic were not used in the re-evaluation as they are not considered representative <br />of MSW in situ. Richardson and Reynolds (1991) reported the results of tests <br />performed on MSW using a 1.5 m by 1.5 m direct shear box. The box was loaded <br />with concrete blocks to normal stresses between 14 and 38 kPa. <br />The data in Table 1 was supplemented by the authors with data from back- <br />analyses of existing MSW landfill slopes known to be stable. Table 2 presents back <br />calculated MSW shear strengths from four existing landfills (GeoSyntec Consultants, <br />1993). <br />TABLE 2 BACK ANALYSIS OF EXISTING LANDFILL SLOPES - <br />AVERAGE MAXIMUM SLOPE WASTE STRENGTH, ¢ <br />SLOPE LANDF1LL <br />Height Slope Height Slope FS = FS= FS= <br />(m) (H'V) (m) (II'V) 1.0 1.1 1.2 <br />Lopez Canyon, CA 120 2.5:1 35 1.7:1 25° 27° 29° <br />OII,CA 75 2:1 20 1.6'1 28° 30° w <br />Babylon, NY 30 1.9: l 10 1.25: l 3QO 34° 38° <br />Private Landfill, OH 40 2:1 10 1.2' 1 30° w 37° <br />Note: FS = Factor of safety for back analysis assuming c = 5 kPa. <br />The back-calculated friction angles for MSW presented in Table 2 were <br />obtained assuming a cohesion of 5 kPa using the modified Bishop method of slices. <br />As the slopes at these landfills have been standing for up to 15 years without <br />excessive deformation or other signs of impending instability, the factors of safety <br />against slope failure within the waste are certainly larger than 1.0 and probably <br />greater than or equal to 1.3. To be conservative, the authors used results for a <br />factor of safety of 1. 2 in the MSW shear strength assessment. <br />The authors assessment of the available shear strength data was performed <br />in a manner similar to Howland and Landva (1992). These investigators presented <br />available data from the technical literature on MSW strength on a plot of shear stress <br />at failure versus normal stress. From the plot, they derived strength parameters that <br />represented the "lower bound" for the entire body of data. These lower-bound <br />strength parameters are strongly influenced by the back-calculated waste strengths