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SLOPE STABILITY EVALUATION FOR
LANDFILL NO. 6 AREA D
VERTICAL INCREASE
Prepared for
EVERGREEN PACKAGING.
CANTON, NORTH CAROLINA
November 2016
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Sevee & Maher Engineers, Inc.
November 2, 2016
TABLE OF CONTENTS
Section No. Title Page No.
1.0 INTRODUCTION............................................................................................................... 1-1
2.0 FIELD INVESTIGATION ................................................................................................... 2-1
3.0 LABORATORY INVESTIGATION .................................................................................... 3-1
4.0 SLOPE STABILITY EVALUATION OF PROPOSED VERICAL INCREASE .................... 4-1
4.1 Methods of Analysis ..........................................................................................4-1
4.2 Selection of Parameters ....................................................................................4-1
4.2.1 Landfill Waste. ............................................................................................4-1
4.2.2 Perimeter Dike. ...........................................................................................4-1
4.2.3 Foundation Materials. ..................................................................................4-2
4.2.4 Cover System. ............................................................................................4-2
4.2.5 Liner. ...........................................................................................................4-2
4.2.6 Piezometric Conditions. ...............................................................................4-3
4.3 Selection of Critical Slope Stability Cross-Section .............................................4-3
4.4 Slope Stability Analyses ....................................................................................4-5
5.0 CONCLUSIONS AND RECOMMENDATIONS ................................................................. 5-1
LIST OF APPENDICES
APPENDIX A BORING LOGS
APPENDIX B LABORATORY TEST RESULTS
APPENDIX C SHEAR STRENGTH SELECTED FOR USE IN THE SLOPE STABILITY
ANALYSIS
APPENDIX D STABILITY ANALYSIS
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LIST OF FIGURES
Figure No. Title Page No.
1 PROPOSED FINAL GRADING PLAN ............................................................................. 1-4
2 INTERPRETIVE GEOTECHNICAL PROFILE A-A’ .......................................................... 4-4
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November 2, 2016
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SLOPE STABILITY EVALUATION FOR
LANDFILL NO. 6 AREA D
VERTICAL INCREASE
This report was prepared to summarize a slope stability evaluation performed for the proposed
vertical increase of the Area D of Landfill No. 6 at the Evergreen pulp and paper making facility
in Canton, North Carolina. The evaluation shows that the height of Area D can be increased by
30 feet with calculated factors of safety for the increase being maintained in excess of 1.8 and
1.3 for post-closure static and earthquake conditions, respectively; and 1.9 for operational
conditions.
1.0 INTRODUCTION
Blue Ridge Paper Products, Inc. (BRPP), doing business as Evergreen Packaging (Evergreen),
owns and operates a 240-acre landfill referred to as Landfill No. 6 (Landfill) in Canton, North
Carolina. The Landfill is used for the disposal of papermill waste including: sludge, lime mud,
boiler ash, and wood waste into discrete containments designated as Areas A, B, C, D, F, G,
and H. In Areas B, C, F, G and H, the operating method was to dump the waste into the
containment(s) and allow it to seek a final configuration by gravity with no supplemental grading
or compaction. This filling practice resulted in a waste mass, which was poorly drained, and of
relatively low shear strength. Because of these conditions, Areas B, C, D, F, G, and H were
originally designed to be filled with waste to elevations no higher than the rim of the perimeter
dikes, which surround each containment.
Evergreen obtained permits from the North Carolina Department of Environmental Quality
(NCDENR) for Area A East and Area A West, which allowed the final waste grade in those
areas to extend to an elevation of 30 feet above the perimeter dikes for those areas. The
permits were based on evaluations presented in SME (1999 and 2006). Area D, although
permitted for final waste grades rising to the level of the rim of its perimeter dike, has been
operated from the outset using waste placement practices intended to maintain a well-drained
and compacted waste mass. Area D contains a leachate collection system that drains the
operating area, allowing operation of trucks, crawler tractors, and other equipment on the waste,
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November 2, 2016
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which, in turn, results in compaction and increased shear strength. Moreover, the waste in
Area D exhibits shear strength similar to that found in previously operated Landfill Areas A East
and A West, for which Evergreen obtained permits to increase the final waste grades to an
elevation 30 feet above the perimeter dikes.
In 2016, Evergreen retained Sevee & Maher Engineers, Inc. (SME) to evaluate the slope
stability of a redesigned Area D, where the waste would extend vertically above the rim of the
existing perimeter dikes. The exterior final waste sideslopes would be sloped at 4 horizontal to
1 vertical (4H:1V), to a maximum final elevation of approximately 2795 feet National Geodetic
Vertical Datum (NGVD), and have 3H:1V interim interior sideslopes where it is anticipated that
the future Area E will overlap a portion of Area D. The proposed final grading plan of Area D is
presented as Figure 1. Like the slope stability evaluation for Areas A-East and A-West,
components of this slope stability evaluation included a field investigation to collect samples of
the waste and perimeter dike soil, laboratory testing of those materials, review of previous site
geotechnical evaluations, interpretation of subsurface conditions, and a slope stability analysis.
In addition to this evaluation of the Area D, several other geotechnical investigations have
previously been conducted at the Landfill. Testing has been performed by SME and others on
the site wastes, landfill foundation and perimeter dike soils. Data from previous SME
investigations and investigations previously conducted by others were used to augment the
findings presented herein, namely:
Design Hydrogeologic Report Addendum for Landfill No. 6 Area D North (SME,
2013)
Geotechnical Evaluation for Landfill No. 6 Area A-West Closure Amendment
(SME, 2011)
Stability Evaluation Landfill No. 6 Site Investigation – Areas D and E (SME,
2008)
Landfill Stability Evaluation for Vertical Expansion Area 6A-West (SME, 2006)
Landfill Stability Evaluation for Vertical Expansions, Area 6A-East (SME, 1999)
Operations Manual, Champion International Corporation Landfill No. 6 East,
Canton, North Carolina, (SME, 1995a)
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Landfill No. 6 Closure Report, Field and Laboratory Investigation Report (SME,
1995b)
Geotechnical Report for Landfill No. 6 Expansion Area A (Sirrine, 1989)
Revised Report of Geotechnical Exploration and Evaluation and Conceptual Site
Development Recommendations, Landfill No. 6 (Law, 1982)
SME
ENVIRONMENTAL CIVIL GEOTECHNICAL WATER COMPLIANCE
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2.0 FIELD INVESTIGATION
Between September 12, 2016 and September 15, 2016, SME conducted a field investigation at
the Landfill, which consisted mainly of drilling five borings at four locations within and around
Area D. These boring locations were designated B16-101 through B16-104 and B16-104A.
Boring B16-101 was drilled into the perimeter dike on the south side of Area D. Borings
B16-102, B16-103, B16-104 and B16-104A were drilled in the Area D waste and terminated
above the existing liner system. Figure 1 shows the boring locations The borings provided
(1) landfill waste and perimeter dike material samples for laboratory testing and visual
examination; (2) in-place shear strength data for the waste; (3) standard penetration test (SPT)
data for the waste and perimeter dike materials; and (4) characterization of the piezometric
conditions within Area D. Boring depths for B16-102, B16-103, B16-104 and B16-104A were
specifically selected to terminate five to ten feet above Area D liner system.
Borehole drilling, temporary piezometer installation and abandonment were performed by A.E.
Drilling Services, LLC of Greenville, South Carolina, (a North Carolina Certified Well
Contractor1) and the work was overseen by SME. The borings were advanced using hollow-
stem auger boring techniques. Logs of the borings are presented in Appendix A. Samples of
the perimeter dike soil were collected using split-spoon sampling methods and waste samples
were collected using both split-spoon and thin-walled (Shelby) tube sampling techniques. In
boring B16-104A, sampling generally alternated between down-hole field vane shear testing,
followed by 3-inch diameter split-spoon sampling (of the shear test interval), and then thin-
walled tube sampling for collection of undisturbed waste specimens. The results of these
sample collection and shear tests are summarized on the boring logs and test reports provided
in Appendix B. Representative waste samples were selected for moisture content, density
determination, and consolidated-undrained (CU) triaxial strength testing. Representative
perimeter dike samples were selected from B16-101 for moisture content testing and a
composite sample was created for direct shear testing. All field and laboratory testing was
1 A.E. Drilling Services, LLC performed all drilling, temporary piezometer installation and abandonment in
accordance with applicable regulations. The driller who performed the work is certified for the work
performed.
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November 2, 2016
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performed in general accordance with applicable American Society for Testing and Materials
(ASTM) or U.S. Army Corps of Engineers (US ACOE) methods.
Temporary standpipe piezometers, identified as P16-102, P16-103 and P16-104, were installed
in borings B16-102, B16-103, B16-104 to measure water levels in the waste2. Each piezometer
consisted of one-inch diameter PVC pipe and slotted screen sections placed at the bottom of
the respective borings. Installation diagrams for the piezometers are included on the boring
logs. Water level measurements were performed in the piezometers during the period of
drilling. No water levels were detected during that time, which was consistent with the condition
of the soil and waste samples as well as the drill cuttings observed during drilling. It also
became evident during drilling that no water table was present within the perimeter dike at B16-
101; therefore, no piezometer was installed at that location.
2 The piezometers were considered temporary, in accordance with North Carolina Well Contractor
Certification Act requirements, and were abandoned in accordance with applicable regulations.
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3.0 LABORATORY INVESTIGATION
Water content, density, specific gravity, and shear strength tests were performed on selected
waste and perimeter dike samples by SME’s geotechnical laboratory in Cumberland, Maine.
The water content of the waste samples tested ranged from about 9 to 107 percent with the
higher water content waste typically associated with shallow depth wastes and waste containing
wood, whereas the lower water content waste was generally from deeper sampling locations
and typically were associated with ash and lime mud. The variability in water content of the
sludge is largely attributable to the process by which it is generated and managed prior to
placement in the landfill as well as the tendency for it to increase in water content as it
degrades. High water content sludge is generally considered soft waste, which is managed as
required in the Operations Manual for the Landfill in order to maintain the slope stability of the
waste mass. The results of the water content testing are included on the boring logs and in
Appendix B. Total unit weight (i.e., density) for the waste was previously calculated using
measured water content and specific gravity data collected in 1995 and averaged 86 pcf. The
specific gravity of three of the waste samples collected in 2016 was determined to be 2.56, 2.26,
and 2.69 (average = 2.50) which in turn resulted in a calculated total unit weight range of 76 and
104 pcf (average = 94 pcf). The results of the specific gravity tests are included in Appendix B.
For purposes of the slope stability evaluation discussed in this report, a waste density of 90 pcf
was selected.
Shear strength of the mixed ash, sludge and lime mud was measured by conducting
consolidated, undrained, triaxial compression tests with pore pressure measurement (CU)
testing on three waste specimens. The results of the CU tests are included in Appendix B. The
testing resulted in a waste effective friction angle of approximately 31 degrees and a cohesion
of 215 psf. These strength values are generally consistent with previous shear strengths
measured for the waste, which have shown effective friction angles ranging from approximately
32 to 58 degrees (Law, 1982; SME, 1995b; SME, 1999; and SME, 2006). Table C-1 and
Figure C-1 of Appendix C summarizes the past and present shear strength testing results for
the waste.
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Shear strength of the perimeter dike soil was measured by direct shear testing of a re-
compacted specimen of composited samples from boring B16-101. The direct shear testing
was performed using a non-inundated (not saturated) condition. The non-inundated condition
was intended to simulate the lack of water table observed in the field. The results of the direct
shear testing are presented in Appendix B. These results are generally consistent with previous
dike soil strength testing which indicated a range of effective friction angles of approximately 30
to 40 degrees with cohesion of up to 620 psf (Law, 1982; Sirrine, 1989; SME, 1999; SME, 2006;
and SME, 2016). Table C-2 and Figure C-2 of Appendix C summarize the past and present
shear strength testing results for the perimeter dike soil.
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Sevee & Maher Engineers, Inc.
November 2, 2016
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4.0 SLOPE STABILITY EVALUATION OF PROPOSED VERICAL INCREASE
4.1 Methods of Analysis
Analyses for the Area D slope stability evaluation were performed using SLOPE/W software.
SLOPE/W effectively analyzes both simple and complex slope configurations for a variety of slip
surface shapes, pore-water pressure conditions, soil properties, and loading conditions. SME
holds an active license with Geo-Slope for use of SLOPE/W. For this evaluation, the Simplified
Bishop and Spencer methods were used to calculate factor of safety solutions for circular and
block shaped failure surfaces, respectively. Slip surfaces were limited to those deeper than five
feet below the surface. For each condition, thousands to tens of thousands of individual slip
surfaces with a wide variety of depths and sizes were evaluated with the minimum value
reported herein. Effective stress was used for the analyses owing to the lack of a water table
being observed in both the exiting Area D waste and its perimeter dike.
4.2 Selection of Parameters
A summary of the soil and waste materials and the associated geotechnical properties used for
conducting the slope stability evaluation are presented in the following sections.
4.2.1 Landfill Waste. The relevant geotechnical properties for the Landfill Waste were
selected based on the laboratory testing reported herein, as well as historical data as discussed
in Section 1.0. The total unit weight and effective strength data for the waste are tabularized on
Table C-1 in Appendix C. The selected effective shear strength for the waste is graphically
presented relative to other available test data on Figure C-1 of Appendix C. The geotechnical
property values selected for the Area D waste were an average total unit weight of 90 pcf and
an average effective friction angle of 32 degrees and no cohesion.
4.2.2 Perimeter Dike. The geotechnical data collected for the Perimeter Dike soils from this
and previous investigations are tabulated on Table C-2 of Appendix C. The direct shear data is
plotted on Figure C-2 of Appendix C, along with available data from previous investigations and
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November 2, 2016
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borrow source investigations completed for other perimeter dikes at the Landfill. The
geotechnical property values selected for the perimeter dike were a total unit weight of 120 pcf
and an effective friction angle of 32 degrees and an effective cohesion of 115 psf.3
4.2.3 Foundation Materials. The foundation materials underlying Area D were assumed to
have a slightly lower friction angle than the dike soils since they have not been mechanically
compacted. The total unit weight and effective friction angles were selected based on
undisturbed tube samples of foundation materials tested by Sirrine, 1989. A total unit weight of
115 pcf and an effective friction angle of 28.5 degrees and no cohesion were selected for use in
the slope stability analyses. The foundation material strength data are graphically presented on
Figure C-3 and tabularized on Table C-3, of Appendix C.
4.2.4 Cover System. The cover system was estimated to have an effective friction angle of 30
degrees and no cohesion, and was assumed to have a unit weight of 125 pcf. The cover
system shear strength is based on the dike soil testing, since the cover is expected to consist
primarily of a similar material to that used for the perimeter dike.
4.2.5 Liner. The Area D liner system consists of 15 inches of #78 stone, underlain by a 16-
ounce geotextile and then a 60-mil HDPE textured geomembrane. On the lower and flatter
portion of the base area, the 60-mil HDPE textured geomembrane is underlain by a
geosynthetic clay liner. The liner system was assigned an overall effective friction angle of 35
degrees and no cohesion, and a unit weight of 125 pcf, based on SME’s experience with similar
materials. This liner strength is higher than the overlying waste, which makes the liner system
inherently more stable than the overlying waste.
3 The act of collecting split spoon samples of the Perimeter Dike results in damage to the large solid
saprolite grains, producing a sample that is finer than actual field conditions. Therefore, strength testing
on this material is biased low, which results in an underestimate of strength that in-turn produces
artificially low factors of safety.
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4.2.6 Piezometric Conditions. A regional phreatic surface, based on water level data
presented by SME in 2013, was used to develop a groundwater phreatic surface (i.e., water
table) in the foundation and dike soils (SME, 2013). The location of the phreatic surface is
included on Figure 2. As indicated in Section 2.0, the perimeter dike boring was observed to be
dry indicating an unsaturated soil condition. The unsaturated observation is consistent with
Area D being a lined containment, represents the design condition, and is also consistent with
historical site information. No phreatic surface was measured in the three piezometers installed
in the Area D waste for this report. The lack of water table in Area D is expected, due to the
extensive drainage placed in that area and adherence with waste management procedures in
the Operations Manual. Accordingly, for the slope stability analyses presented herein, the
waste in Area D (both current and proposed) was treated as being unsaturated to represent the
design condition.
It should be noted that although the described unsaturated piezometric conditions were
observed and are expected to be present in the Area D waste, the slope stability evaluation also
analyzed a hypothetical fully-saturated waste mass with a phreatic surface near the top of the
waste. This assumed condition is considered conservative in that the waste mass would be
undrained and the leachate collection system inoperable, making this analysis not
representative of design conditions.
4.3 Selection of Critical Slope Stability Cross-Section
One critical cross-section (i.e., Cross-Section A-A’) was selected as representative of the worst-
case geometry for Area D, relative to slope stability. The cross-section is presented in Figure 2,
and the cross-section location is shown on Figure 1. Cross-Section A-A’ was selected as critical
for the following reasons: (1) it passes through the area with the proposed greatest waste
thickness and steepest sloping base grades; and (2) it provides the greatest vertical change
over the shortest distance between the highest waste grades (~Elevation 2795) and the edge of
Landfill (~ Elevation 2658).
NOTES:
Soil Cover
Waste
Liner System
Foundation Material
Perimeter Dike
Bedrock
125
90
125
115
120
Impenetrable
30
32
35
31.5
32
0
0
0
0
115
Material Total Unit Weight
(pcf)
Effective
Friction
Angle
(degrees)
Effective
Cohesion
(psf)
Number and Color
1
2
4
5
6
3
NOTES:
The surface of Material 3 (Waste) is based on the topographic Survey dated 1/29/2016.
Phreatic surface, applied to Foundation Material and Perimeter Dike as indicated in Appendix D.SME
ENVIRONMENTAL CIVIL GEOTECHNICAL WATER COMPLIANCE
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Sevee & Maher Engineers, Inc.
November 2, 2016
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4.4 Slope Stability Analyses
Effective stress conditions were used in the slope stability analysis. This approach is
appropriate for free-draining materials such as the wastes landfilled in Area D. As described
above, shear strengths were selected from the testing of the waste and dike materials. SME
performed both static (i.e., non-earthquake) and seismic (i.e., earthquake) slope stability
analyses for the proposed loads resulting from the final grading for Area D as shown on
Figure 1.4 The seismic analysis consisted of a pseudo-static analysis in which a horizontal force
is applied to the static model to simulate earthquake acceleration5. The results of the slope
stability analyses are included in Appendix D and indicate adequate factors of safety for the
proposed final grading configuration after closure of Area D. The calculated minimum factors of
safety for the design conditions are summarized in Table 4-1. The factors of safety were
calculated for three types of potential slip surface: (1) surfaces passing through the waste
alone; (2) surfaces passing through the waste, perimeter dike and foundation soil; and (3)
deeper surfaces passing through the waste and foundation soil. Potential slip surfaces through
the liner system were considered; however, due to the landfill configuration and higher liner
strength than that of the overlying waste, as described in Section 4.2.5, the factors of safety for
slip surfaces through the waste will be lower than those passing through the waste and liner
system. Factors of safety were calculated for potential slip surfaces moving from: (a) south to
north (i.e., right to left on Cross-Section A-A’), which evaluated the operational slope stability of
4 A new landfill area north of Area D, called Area E is being planned. For this analysis, closure of the
northern slope of Area D is not assumed, since this area is anticipated to be covered with waste as part
of Area E. Should Area E not be constructed, a closure stability analysis for the northern slope of Area
D North should be performed.
5 The seismic slope stability analyses followed the approach outlined in U.S.EPA Subtitle D – Design
Guidance. Based on the work of Hynes and Franklin, 1984, for a factor of safety greater than or equal
to 1.0, a maximum value of the seismic coefficient used in the pseudo-static analysis was one-half the
maximum acceleration estimated at the base of the landfill in order to keep permanent cover and
embankment deformations less than 12 inches after an earthquake. Six to 12 inches of seismically
induced downslope displacement is generally considered tolerable in the design of landfill liners (Seed
and Bonaparte, 1992). The maximum horizontal seismic acceleration (a.k.a., peak ground acceleration)
at the Area D site was obtained from 2014 U.S Geological Survey Seismic Hazard Maps. This map
provides a maximum acceleration at the bedrock surface of 0.26g (acceleration, as a percent of gravity)
in the western North Carolina region, with a 90 percent probability of not being exceeded in 250 years.
Based on Hynes and Franklin, 1984, the seismic coefficient to be used in the pseudo-static slope
stability analysis is one-half of 0.26g or 0.13g.
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the northern slope during operations and (b) north to south (i.e., left to right on cross-section A-
A’), which evaluated the post-closure slope stability of the southern end of Area D (i.e., the side
closest to the Pigeon River).
TABLE 4-1
SUMMARY OF MINIMUM FACTORS OF SAFETY
Potential Slip
Surface Type
Slip Surface Movement
Direction and
(Condition)
Piezometric
Condition
(See Note 1)
Minimum Calculated
Factor of Safety and
(Slip Shape)
Results Located
in Appendix D,
on page1
Static Seismic
Waste North to South
(Post-Closure)
Unsaturated
Waste
2.4
(Circular)
1.5
(Circular)
1 – 4
Waste South to North
(Operational)
Unsaturated
Waste
1.9
(Circular)
NA 5 & 6
Waste, Perimeter
Dike and Foundation
North to South
(Post-Closure)
Phreatic in
Foundation
1.7
(Block)
1.4
(Block) 7 - 10
Waste and
Foundation
North to South
(Post-Closure)
Phreatic in
Foundation
2.5
(Block)
1.5
(Block) 11 & 12
Waste and
Foundation
South to North
(Operational)
Phreatic in
Foundation
2.1
(Circular) NA 13 & 14
Notes:
1. The piezometric condition is represented by the dashed blue lines in Appendix D, which represent the phreatic
surface in the specific materials.
2. Some of the results are provided on two separate pages, including the first showing the entire cross-section and
the second zoomed in on the slip surface for clarity.
Generally, factors of safety greater than 1.5 for post-closure and 1.3 for operational static cases
and 1.0 for seismic cases are considered acceptable to the professional engineering community
for slope stability evaluations. Since the seismic factors of safety calculated for the Area D
slope stability exceed 1.0, permanent seismic deformations are expected to be less than 6
inches and are not expected to damage to the leachate collection system, liner or landfill slopes
should earthquake conditions occur (Seed and Bonaparte, 1992).
The sensitivity analysis, which evaluated a static fully-saturated waste mass with a phreatic
surface at the top of the waste, yielded factors of safety of 1.2 or better for circular slip surfaces
within the waste for slip surfaces moving from north to south (see Appendix D, pages 15 and
16). This demonstrates that under this un-realistic condition, the waste was will remain stable
and not experience unacceptable movement beyond the confines of the Area D containment.
For slip surface moving from south to north (see Appendix D, pages 17 and 18), the saturated
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waste condition would result in a factor of safety less than 1.0, indicating that as the waste
saturates it may slough inside the containment, as expected. The Operations Manual includes
a requirement that waste be kept back at least 25 feet from the northern containment berm for
just such an unexpected condition; therefore, even under this unrealistic situation the design
ensures that the waste will remain within the containment.
The critical slip surfaces in the waste are shallow and approach the infinite slope condition,
which yields the lowest possible factor of safety for the sloped waste, with deeper surfaces
indicating higher factors of safety. An infinite-slope analysis (Lambe and Whitman, 19696) was
used to check the slope stability of the face of the closed landfill and cover (see Appendix D,
pages 1 and 3). Based on discussions with Evergreen, it is expected that a cover system will be
used for closure of Area D. No specific final cover system slope stability analysis was
performed for this report other than this infinite slope analysis and inclusion of the cover in
evaluation of post-closure-slope stability. Based on the selected shear strengths, and assuming
no seepage parallel to the landfill slope faces, a minimum factor of safety of 2.3 was calculated,
which is considered acceptable.
6 The infinite slope factor of safety is equal to {Tangent (effective friction angle) / Tangent (slope angle)};
results are shown in Appendix D on pages 1 and 3 for the waste and cover.
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5.0 CONCLUSIONS AND RECOMMENDATIONS
Based on the observations made at the Landfill, interpretation of the available field and
laboratory test data, and the results of the slope stability evaluation completed for this report,
the following conclusions and recommendations have been reached.
The critical cross-section used in the analysis was selected to represent the
worst-case slope conditions, which will produce the lowest factors of safety, due
to the slope height and geometry. Therefore, the factors of safety presented
herein are considered the minimum values with higher factors of safety for
typically deeper slip surfaces yielding higher factors of safety.
The results of the static and seismic slope stability analyses conducted for the
proposed final grading plan for Area D exceed accepted safety factors for the
worst-case slope stability cross-section analyzed. Accordingly, it is concluded
that stable slope, foundation, and waste conditions will be maintained using the
proposed final grading and waste streams described in this report.
Future wastes delivered to the landfill are assumed to consist mainly of the same
sludge, ash, and lime mud as has historically been placed in Area D. It is
recommended that if the future waste stream changes in apparent strength or
character, or if saturation of the waste changes from that described within this
report, then a reevaluation of the landfill slope stability should be conducted.
A revised Operations Manual for Landfill No. 6, including Area D Vertical
Increase, will be issued under separate cover. It is recommended that layering of
the ash and sludge continue during landfilling operations to maintain slope
stability and otherwise follow the recommendations set forth in the Operations
Manual, including the placement of any lower strength waste within the interior
portion of the landfill, not less than 100 feet from the exterior slope faces.
In conducting the subsurface investigation, laboratory testing, engineering
evaluation and reporting, SME endeavored to work in accordance with generally
accepted professional geotechnical and geologic practices and principles
consistent with the level of care and skill ordinarily exercised by members of the
geotechnical profession currently practicing in same locality under similar
____________________
161028brpp-6D-VI-lfstab
Sevee & Maher Engineers, Inc.
November 2, 2016
5-2
conditions. No other warranty, expressed or implied is made. During final
design, construction and/or operations, if conditions are encountered which
appear different from those described in this report7, SME requests that it be
notified so that the evaluation and recommendations presented herein can be
reviewed and modified as appropriate.
7 Differences that could affect slope stability include but are not limited to things like slope geometry,
waste properties, soft waste management, and waste saturation.
____________________
161028brpp-6D-VI-lfstab
Sevee & Maher Engineers, Inc.
November 2, 2016
REFERENCES
Hynes, M.E. and A.G. Franklin, 1984. Rationalizing the Seismic Coefficient Method,
Miscellaneous Paper GL-84-13, U.S. Army Engineer Waterways Experiment Station, Vicksburg,
Mississippi, 34p.
Lambe, T.W. and R.V. Whitman, 1969. Soil Mechanics; John Wiley & Sons, New York.
Law, 1982. Revised Report of Geotechnical Exploration and Evaluation and Conceptual Site
Development Recommendations, Landfill No. 6.
Seed, R.B. and R. Bonaparte, 1992. Seismic Analysis and Design of Lined Waste Fills:
Current Practice. Proc. Stability and Performance of Slopes and Embankments - II, Vol. 2,
ASCE Geotechnical Special Publication No. 31, Berkeley, California, pp.1521-1545.
SME, 1995a. Operations Manual, Champion International Corporation Landfill No. 6 East,
Canton, North Carolina.
SME, 1995b. Landfill No. 6 Closure Report, Field and Laboratory Investigation Report.
SME, 1999. Landfill Stability Evaluation for Vertical Expansion, Area 6A-East.
SME, 2006. Landfill Stability Evaluation for Vertical Expansion, Area 6A-West.
SME, 2008b. Stability Evaluation Landfill No. 6 Site Investigation – Areas D and E.
SME, 2013. Design Hydrogeologic Report Addendum for Landfill No. 6, Area D North
Sirrine, 1989. Geotechnical Report for Landfill No. 6 Expansion Area A.
U.S.EPA, 1995. RCRA Subtitle D (258) Seismic Design Guidance for Municipal Solid Waste
Landfill Facilities. United States Environmental Protection Agency, April.
APPENDIX A
BORING LOGS
PROJECT: Evergreen Packaging Phase 6D-Vertical Expansion Investigation JOB NO.: 16144.00
DATE STARTED: 09/12/2016 DATE FINISHED: 09/13/2016 DRILLING METHOD: 3.25 ID HSA
GROUND SURFACE ELEVATION (FT): 2659.8 DRILLING CONTRACTOR: A.E. Drilling Services, LLC LOGGED BY: BBJ of Sevee & Maher Engineers, Inc.
Auger Refusal Depth: Not Encountered Rock Core Interval: None SPT with Automatic Hammer SHEET 1 OF 1
DEPTH
(FT)
SAMPLE
NO.
Sample
Interval
Geologic
Unit
SPT Blows per
6-inch Interval
(See Note 2)
SPT
N-VALUE
(bpf)
Recovery
Penetration
(feet)
Field
Testing
Lab
Testing
(see Note 2)
Piezometer
Log
DEPTH
(FT)
(See Note 3)
5
10
15
20
25
30
35
40
45
50
NOTES:
2. Lab Testing: %w = water content (ASTM D-2216); DS = Direct Shear (ASTM D-3080) on composite of recovered soils.
3. Boring was damp at the end of drilling and the following morning; therefore, no piezometer was installed. Exploration backfilled with auger cuttings.
S-2
1. The act of collecting the samples with a standard split spoon broke-down the re-compacted saprolite and yielded samples that as described below are finer in texture
than exist in the dike, with the material more a Silty SAND with occasional gravel-sized particles.
BORING NO.: B16-101
MATERIAL DESCRIPTION
(See Note 1)
S-1 3 - 5
Gray, Gravel (Road fill); Cuttings: Rust colored,
SILT, little fine to medium sand, trace fine gravel
and coarse sand, damp.
8/3/5/6 8 0.2/2.0
S-3 13 - 15
Rust colored to Brown, micaceous SILT, little fine to
medium sand, trace coarse sand to fine gravel,
damp.
7/7/6/8 13
8 - 10 Cuttings: Brown to Rust colored, SILT, little fine
sand to coarse gravel, damp.8/7/9/10 16 0.0/2.0
1.0/2.0
Similar to above. 4/6/5/5 11 1.8/2.0
1.2/2.0
1.0/2.0S-5 23 - 25 Similar to above. 14/13/11/11 24
S-6 28 - 30 Similar to above, slightly damp. 5/7/6/7 13
Saprolite
24 1.6/2.0
S-10 48 - 50 Similar to above. 4/4/8/9 12 1.4/2.0
S-9 43 - 45 6/9/15/20
19.2%w
S-4
S-8 38 - 40
Rust colored to brown, SILT, little fine to coarse
sand; trace white with black specks (weathered
granite) and mica, damp and crumbly.
10/11/12/14 23
Perimeter
Dike
Compacted
Saprolite
(Fill)
18 - 20
2.0/2.0
43-44': Similar to above.
S-7 34 - 36
Similar to above, yellow/brown layers at 35.5 - 36
feet.19/10/10/14 20
12.9%w
13.6%w
9.4%w
15.7%w
12.9%w
15.6%w
15.2%w
16.7%w
18.1%w
BOTTOM OF EXPLORATION AT 50 FEET
44-45': Rust colored to Brown, Saprolite
(micacious silty sand), damp.
0.4/2.0
\\nserver\CFS\Brpp\NC\Vertical Increase\SSI\Boring Log\blue ridge borings 2016
Page 1 of 5
PROJECT: Evergreen Packaging Phase 6D-Vertical Expansion Investigation JOB NO.: 16144.00
DATE STARTED: 09/13/2016 DATE FINISHED: 09/13/2016 DRILLING METHOD: 3.25 ID HSA
GROUND SURFACE ELEVATION (FT): 2689.8 DRILLING CONTRACTOR: A.E. Drilling Services, LLC LOGGED BY: BBJ of Sevee & Maher Engineers, Inc.
Auger Refusal Depth: Not Encountered Rock Core Interval: None SPT with Automatic Hammer SHEET 1 OF 1
DEPTH
(FT)
SAMPLE
NO.
Sample
Interval
Geologic
Unit
SPT Blows per
6-inch Interval
(See Note 1)
SPT
N-VALUE
(bpf)
Recovery
Penetration
(feet)
Field Testing
(See Note 4)
Lab
Testing
(See Note 2)
P16-102
Piezometer
Log
(See Note 3)
DEPTH
(FT)
5
10
15
20
25 PP: 0.25 TSF 94.3%w
PP: 1.25 TSF 43.0%w
29
30 PP: 0.50 TSF 51.0%w
PP: 0.25 TSF 61.8%w
31
34
35 PP: 0.25 TSF 47.4%w
Not Cohesive 34.3%w
40 Not Cohesive
PP: 0.25 TSF 51.7%w
43
45
NOTES:
1. Values are blows per 6-inch interval; or WOR = Weight of Rods
3. Boring was dry at the end of drilling, temporary piezometer was dry for 2 days following drilling. Piezometer abandoned 9/15/2016 by pulling PVC and grouting.
4. Field Testing Included: PP = Pocket Penetrometer.
2. Lab Testing: %w = water content (ASTM D-2216)
BORING NO.: B16-102
MATERIAL DESCRIPTION
S-1 4 - 6 Black and Blue, ASH and LIME, wet. 3/2/2/3 4 2.0/2.0 PP: 1.25-1.5 TSF 52.4%w
S-2 9 - 11 Black, ASH, trace lime, wet. 1/WOR/1/1 1 2.0/2.0 PP: 0.5-1.0 TSF 61.9%w
PP: 1.0-2.0 TSF 51.1%w
1.5/2.0 PP: 0.25-0.5 TSF 87.9%w
S-3 14 - 16 Black and Blue, ASH and LIME, 3-inch layers, wet. 2/1/2/2 3 2.0/2.0
S-4 19 - 21 Black, ASH, trace wood chips, wet. 1/1/1/1 2
24 - 26 1/3/3/8 6 2.0/2.0
24-25': Black, ASH, wet.
25-24': Blue, LIME, trace ash, wet.
S-7 34 - 36 1/2/18/21 20 2.0/2.0
34-35': Black, LIME, saturated.
35-36': Black, ASH with sawdust, gravel in 3-inch
layers, wet.
Papermill
Wastes
S-6 29 - 31 2/2/3/4 5 2.0/2.0
29-30': Black, ASH, wet.
30-31': Blue, LIME, dilatent, wet.
S-5
Filter Sand
1" diam.
PVC
0.001"
Slotted
Screen
Bentonite
Chips
1" diam.
PVC Riser
Backfilled
with Neat
Cement
Grout
BOTTOM OF EXPLORATION AT 43 FEET
S-8 39 - 41 4/3/1/2 4 2.0/2.0
39-40': Black, ASH with sawdust and wood, gravel
in 3-inch layers, wet.
40-41': Gray, SLUDGE; wet.
\\nserver\CFS\Brpp\NC\Vertical Increase\SSI\Boring Log\blue ridge borings 2016
Page 2 of 5
PROJECT: Evergreen Packaging Phase 6D-Vertical Expansion Investigation JOB NO.: 16144.00
DATE STARTED: 09/12/2016 DATE FINISHED: 09/13/2016 DRILLING METHOD: 3.25 ID HSA
GROUND SURFACE ELEVATION (FT): 2686.2 DRILLING CONTRACTOR: A.E. Drilling Services, LLC LOGGED BY: BBJ of Sevee & Maher Engineers, Inc.
Auger Refusal Depth: Not Encountered Rock Core Interval: None SPT with Automatic Hammer SHEET 1 OF 1
DEPTH
(FT)
SAMPLE
NO.
Sample
Interval
Geologic
Unit
SPT Blows per
6-inch Interval
SPT
N-VALUE
(bpf)
Recovery
Penetration
(feet)
Field Testing
(See Note 3)
Lab
Testing
(See Note 1)
P16-103
Piezometer
Log
(See Note 2)
DEPTH
(FT)
5
10 PP: 0.25 TSF 47.3%w
Not Cohesive 9.2%w
15
20
25
26
29
30 PP: 0.25 TSF Not Tested
PP: 0.5 TSF 83.3%w 31
PP: 0.5 TSF 50.7%w
35 PP: 0.75 TSF 47.2%w
Not Cohesive 20.0%w
40 Not Tested 55.7%w
Not Cohesive 106.5%w 41
45
NOTES:
2. Boring was dry at the end of drilling, temporary piezometer was dry for 2 days following drilling. Piezometer abandoned 9/15/2016 by pulling PVC and grouting.
3. Field Testing Included: PP = Pocket Penetrometer.
1. Lab Testing: %w = water content (ASTM D-2216)
BORING NO.: B16-103
MATERIAL DESCRIPTION
S-1 4 - 6 Blue/Green, LIME, wet. 1/1/1/2 2 2.0/2.0
S-3 14 - 16 Black and Blue, ASH, little Lime, wet. 1/2/2/3 4
2.0/2.0
9 - 11 27 2.0/2.0
S-4 19 - 21
Black with Blue, ASH, trace lime, wet; hard layer at
20 ft.1/1/1/1 2
S-2
50.0%w
PP: 0.5 TSF 55.7%w
S-8 39 - 41 1/3/2/3 5.0
S-7 34 - 36 1/2/5/3 7 1.8/2.0
S-6 29 - 31 1/1/2/3
1/12/15/13
1" diam.
PVC Riser
34-34.5': Black and Blue, ASH, trace lime, wet.
34.5-35': Gray SLUDGE.
35-36': Black, Cinders.
Papermill
Wastes
29-30 ft: Simmilar to above
30-31 ft: Black, ASH, trace wood fibers, wet.
39-40': Black and Blue; ASH and LIME, wet.
40-41': Wood with ASH, wet.
Simmilar to above.
Black, ASH, with coal and wood, hard.
PP: 0.25-0.5 TSF 54.6%w
PP: 0.25 - 0.5 TSF 60.4%w
PP: 0.75 TSF
Filter Sand
Backfilled
with Neat
Cement
Grout
BOTTOM OF EXPLORATION AT 41 FEET
Bentonite
Chips
1" diam.
PVC
0.001"
Slotted
Screen
1.6/2.0
3 2.0/2.0
2.0/2.0
2.0/2.0
S-5 24 - 26 Simmilar to above, no hard layer. 3/4/3/5 7
\\nserver\CFS\Brpp\NC\Vertical Increase\SSI\Boring Log\blue ridge borings 2016
Page 3 of 5
PROJECT: Evergreen Packaging Phase 6D-Vertical Expansion Investigation JOB NO.: 16144.00
DATE STARTED: 09/13/2016 DATE FINISHED: 09/13/2016 DRILLING METHOD: 3.25 ID HSA
GROUND SURFACE ELEVATION (FT): 2703.9 DRILLING CONTRACTOR: A.E. Drilling Services, LLC LOGGED BY: BBJ of Sevee & Maher Engineers, Inc.
Auger Refusal Depth: Not Encountered Rock Core Interval: None SPT with Automatic Hammer SHEET 1 OF 1
DEPTH
(FT)
SAMPLE
NO.
Sample
Interval
Geologic
Unit
SPT Blows per
6-inch Interval
(See Note 1)
SPT N-
VALUE
(bpf)
Recovery
Penetration
(feet)
Field Testing
(See Note 4)
Lab Testing
(See Note 2)
P16-104
Piezometer
Log
(See Note 3)
DEPTH
(FT)
5
10
Not Tested
15 52.7%w
20
PP: 1.25 TSF 49.6%w
25 PP: 1.25 TSF 43.1%w
30
PP: 0.5 TSF Not Tested
35 PP: 2.5 TSF 35.0%w
36
38
40 40
PP: 0.25 TSF
45 PP: 2.5 TSF
Not Tested Not Tested
Not Tested 49.7%w
50 Not Cohesive Not Tested 50
NOTES:
1. Values are blows per 6-inch interval; or WOR = Weight of Rods
3. Boring was dry at the end of drilling, temporary piezometer was dry for 2 days following drilling. Piezometer abandoned 9/15/2016 by pulling PVC and grouting.
4. Field Testing Included: PP = Pocket Penetrometer.
2. Lab Testing: %w = water content (ASTM D-2216)
BORING NO.: B16-104
MATERIAL DESCRIPTION
S-1 3 - 5 Black, ASH, trace Lime, moist. 2/2/1/2 3 1.2/2.0 PP: 0.5 TSF 42.5%w
S-2 8 - 10 Gray-Black, ASH, moist. WOR/WOR/1/1 1 1.8/2.0 PP: 0.5 TSF 76.3%w
S-3 13 - 15 1/2/1/2 3 2.0/2.0
13-14': Simmilar to above.
14-15': Blue, LIME, wet.PP: 1.5 TSF
S-4 18 - 20 Blue, LIME, little Ash, wet. WOR/1/1/1 2
S-5 23 - 25
23-24': Similar to above.2/3/2/4 524-25': Gray/Blue, LIME, wet.
Bentonite
Chips
S-7 33 - 35
33-34': Black, ASH, soft, wet.1/6/13/13 19 2.0/2.034-35': Black, ASH, very hard, wet.
49.5-50': Black; ASH, with sawdust and wood chips,
wet.
Gray, LIME, wet.
Blue and Black, ASH and LIME, wet.S-8 38 - 40
S-6 28 - 30
1" diam.
PVC
0.001"
Slotted
Screen
Filter Sand
53.2%w
BOTTOM OF EXPLORATION AT 50 FEET
S-9 43 - 45
S-10 48 - 50
3/5/12/12 17 1.8/2.0
Papermill
Wastes
48-49': Black and Blue, ASH and LIME, wet.
50.8%w
49-49.5': Gray SLUDGE, wet.
Black and Blue, ASH and LIME, soft at top and hard
at bottom, wet.
PP: 0.25 TSF 63.0%w
PP: 0.25-0.50 TSF 62.2%w1/WOR/WOR/1 WOR 2.0/2.0
WOR/WOR/1/W
OR 1 2.0/2.0
1" diam.
PVC Riser
PP: 1.25 TSF
2.0/2.0
2.0/2.0
Backfilled
with Neat
Cement Grout
\\nserver\CFS\Brpp\NC\Vertical Increase\SSI\Boring Log\blue ridge borings 2016
Page 4 of 5
PROJECT: Evergreen Packaging Phase 6D-Vertical Expansion Investigation JOB NO.: 16144.00
DATE STARTED: 09/13/2016 DATE FINISHED: 09/13/2016 DRILLING METHOD: 3.25 ID HSA
GROUND SURFACE ELEVATION (FT): 2703.9 (approx)DRILLING CONTRACTOR: A.E. Drilling Services, LLC LOGGED BY: BBJ of Sevee & Maher Engineers, Inc.
Auger Refusal Depth: Not Encountered Rock Core Interval: None SPT with Automatic Hammer SHEET 1 OF 1
DEPTH
(FT)
SAMPLE
NO.
Sample
Interval
Geologic
Unit
Recovery
Penetration (feet)
Field Testing
(See Note 4)
Lab Testing
(See Note 2)
Piezometer
Log
DEPTH
(FT)
(See Note 3)
5
V-1 & S-1 6 - 7
V-2 & S-1 7 - 8
10
15
V-3 & S-2 16 - 17
V-4 & S-2 17 - 18
20
25
V-5 & S-3 26 - 27
V-6 & S-3 27 - 28
30
V-7 & S-4 30 - 31
V-8 & S-4 31 - 32
35
V-9 & S-5 36 - 37
V-10 & S-5 37 - 38
40
45
50
NOTES:
2. Lab Testing: %w = water content (ASTM D-2216); SG = Specific Gravity; CU = Consolidated Undrained Triaxial Compression; DS = Direct Shear; T = Total Density (direct measure).
3. No piezometer installed, due to proximity to B16-104.
4. Field Testing Included: PP = Pocket Penetrometer.
U-4R 40 - 42
60.4 to 85.2%w
23.8 to 65.9%w
CU#3: 50%w,
102.1T & 2.69SG
BORING NO.: B16-104A
MATERIAL DESCRIPTION
(See Note 1)
Gray, SLUDGE and ASH, moist. NA PP: 0.25-0.5 TSF 47.0%w
Field Vane (FV) Shear Test
(Peak/Remoulded)
PP: 0.50-0.75 TSF 42.6%wFV: 1000/428 psf
Sample Disturbed
by Vane Testing.41.9%wFV:857/514 psf
U-3 28 - 30 Tube had long void, likely from pushing wood/rock
Papermill
Wastes
U-2 18 - 20
U-1
See Tube Opening Summary 1.75/2.0
FV: 514/114 psf
FV: 628/143 psf
Black, ASH, trace Lime, wet.
1. 3-inch diameter split spoons were pushed over the interval where vane shear testing was performed, to provide sample for description, field testing and lab testing.
No Recovery FV: 971/571 psf NA No Recovery No RecoveryFV: 1028/400 psf
Black, ASH, trace Lime, wet.
BOTTOM OF EXPLORATION AT 42 FEET
U-4
CU#2: 74.1%w,
75.6T & 2.26SG
CU#1:48.5%w,
103.6T & 2.56SG
Sample Disturbed by Vane Testing.41.9%wFV: 628/200 psf
FV: 657/371 psf
8 - 10 See Tube Opening Summary 1.2/2.0
See Tube Opening Summary 1.85/2.0
NA
38 - 40 No Recovery
NA
Black, ASH, trace Lime, wet.FV: 1000/857 psf NA
FV: 2342/571 psf
\\nserver\CFS\Brpp\NC\Vertical Increase\SSI\Boring Log\blue ridge borings 2016
Page 5 of 5
APPENDIX B
LABORATORY TEST RESULTS
BRPP/NC/Vertical Increase/Geotech/Appx B lab test results.pdf Page 1 of 13
B
R
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BRPP/NC/Vertical Increase/Geotech/Appx B lab test results.pdf Page 5 of 13
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P
a
g
e
7
o
f
1
3
B
R
P
P
/
N
C
/
V
e
r
t
i
c
a
l
I
n
c
r
e
a
s
e
/
G
e
o
t
e
c
h
/
A
p
p
x
B
l
a
b
t
e
s
t
r
e
s
u
l
t
s
.
p
d
f
P
a
g
e
8
o
f
1
3
BRPP/NC/Vertical Increase/Geotech/Appx B lab test results.pdf Page 9 of 13
BRPP/NC/Vertical Increase/Geotech/Appx B lab test results.pdf Page 10 of 13
BRPP/NC/Vertical Increase/Geotech/Appx B lab test results.pdf Page 11 of 13
BRPP/NC/Vertical Increase/Geotech/Appx B lab test results.pdf Page 12 of 13
BRPP/NC/Vertical Increase/Geotech/Appx B lab test results.pdf Page 13 of 13
APPENDIX C
SHEAR STRENGTH SELECTED FOR USE IN THE
SLOPE STABILITY ANALYSIS
\\nserver\CFS\Brpp\NC\Vertical Increase\Geotech\Material Strengths 2016a
Tab: F‐C‐1 Waste
0
1000
2000
3000
4000
5000
6000
7000
8000
0 1000 2000 3000 4000 5000 6000 7000 8000
Ef
f
e
c
t
i
v
e
Sh
e
a
r
St
r
e
s
s
,
(p
s
f
)
Effective Normal Stress, (psf)
Law, 1982, Assumed Waste, CU Test (φ' = 45°, c' = 50 psf)
SME, 1995, Sludge/Ash, CU Test (φ' = 43.7°, c' = 0 psf)
SME, 1995, Sludge/Ash, CU Test (φ' = 39.5°, c' = 0 psf)
SME, 1995, Sludge/Ash, CU Test (φ' = 39.3°, c' = 0 psf)
SME, 1995, Sludge/Ash, CU Test (φ' = 35.7°, c' = 0 psf)
SME, 1999, Lime Mud, CU Test (φ' = 39.5°, c' = 0 psf)
SME, 1999, Sludge/Ash, CU Test (φ' = 57.9°, c' = 0 psf)
SME, 1999, Sludge/Ash, CU Test (φ' = 45.6°, c' = 0 psf)
SME, 2006, Sludge/Lime/Ash, CU Test (φ' = 36.9°, c' = 0 psf)
SME, 2016, Lime w/ gravel layer, B16‐104A, CU‐20psi
SME, 2016, Lime/Ash, B16‐104A, CU‐30psi
SME, 2016, Ash/Sludge/Bark, B16‐104A, CU‐40psi
Used in Stability Analysis (φ' = 32°, c' = 0 psf)FIGURE C‐1
Plot of Available effective Shear Strengths for Landfill Waste
Landfill 6 Area D ‐Vertical Increase
Evergreen Products
Canton, North Carolina
Sevee & Maher Engineers, Inc.
Page 1 of 6
\\nserver\CFS\Brpp\NC\Vertical Increase\Geotech\Material Strengths 2016a
Tab: F‐C‐2 Dike
0
1000
2000
3000
4000
5000
6000
7000
8000
0 1000 2000 3000 4000 5000 6000 7000 8000
Sh
e
a
r
St
r
e
s
s
,
(p
s
f
)
Normal Stress, (psf)Sirrine, 1989, CU Test (φ = 40°, c = 0 psf)
Sirrine, 1989, CU Test (φ = 32°, c = 115 psf)
Law, 1982, CU Test (φ = 32°, c = 0 psf)
Law, 1982, CU Test (φ = 30°, c = 0 psf)
Law, 1982, CU Test (φ = 40°, c = 0 psf)
SME, 1999, Direct Shear Test (Dry), Normal Stress <2200 psf (φ = 38°, c = 0 psf)
SME, 1999, Direct Shear Test (Dry), Normal Stress > 2200 psf (φ = 34°, c = 260 psf)
SME, 2006, Direct Shear Test (Dry) (φ = 32°, c = 144 psf)
SME, 2016, Direct Shear Tests (Dry)
Used in Stability Analysis (φ = 32°, c = 115 psf)
FIGURE C‐2
Plot of Available effective Shear Strengths for Perimeter Dikes
Landfill 6 Area D ‐Vertical Increase
Evergreen Products
Canton, North Carolina
Sevee & Maher Engineers, Inc.
Page 2 of 6
\\nserver\CFS\Brpp\NC\Vertical Increase\Geotech\Material Strengths 2016a
Tab: F‐C‐3 Foundation
0
1000
2000
3000
4000
5000
6000
7000
8000
0 1000 2000 3000 4000 5000 6000 7000 8000
Sh
e
a
r
St
r
e
s
s
,
(p
s
f
)
Normal Stress, (psf)
LAW, 1982, CU Test (φ = 34°, c = 200 psf)
LAW, 1982, CU Test (φ = 31.5°, c = 100 psf)
LAW, 1982, CU Test (φ = 28.5°, c = 600 psf)
Used in Stability Analysis (φ = 31.5°, c = 0 psf)
FIGURE C‐3
Plot ofAvailable effective Shear Strengths for Foundation Materials
Landfill 6 Area D ‐Vertical Increase
Evergreen Products
Canton, North Carolina
Sevee & Maher Engineers, Inc.
Page 3 of 6
Fr
i
c
t
i
o
n
An
g
l
e
(d
e
g
r
e
e
s
)
Co
h
e
s
i
o
n
(p
s
f
)
Fr
i
c
t
i
o
n
An
g
l
e
(d
e
g
r
e
e
s
)
Co
h
e
s
i
o
n
(p
s
f
)
1
B
u
l
k
#1
64
1
6
0
57
0
Sludge, UU
1
Bu
l
k
#2
82
1
6
0
55
0
Sludge/Ash, UU
1
Bu
l
k
#3
68
9
0
11
0
0
Sludge/Ash, UU
1
Sa
m
p
l
e
#1
N/
A
40
2
0
0
S
l
u
d
g
e
,
Compaction Test
1
Sa
m
p
l
e
#2
N/
A
Sl
u
d
g
e
/
A
s
h
,
Compaction Test
2
55
45
5
0
Assumed Waste, CU
3
B
1
0
1
1
S
1
3
.
5
N
/
A
7
9
3
5
.
7
0
Ash, CU
3
B
1
0
1
3
S
3
2
.
5
7
8
7
9
3
9
.
3
0
Sludge/Ash, CU
3
B
1
0
1
4
S
4
0
.
5
8
0
7
5
4
3
.
7
0
Sludge/Ash, CU
3
B
1
0
2
1
S
1
2
.
5
N
/
A
7
9
3
9
.
5
0
Ash, some Sludge
3
96
5
4
Li
m
e
mud, Density Test
4
B
9
9
‐10
2
U
2
2
0
.
5
8
5
7
1
.
1
4
5
.
6
0
Sludge/Ash, CU
4
B
9
9
‐10
2
U
3
3
0
.
6
7
8
7
7
.
6
5
7
.
9
0
Sludge/Ash, CU
4
B
9
9
‐10
3
U
4
4
0
.
5
9
6
39
.
5
0
Lime mud, CU
5B
‐06
‐01
1
S
6
.
5
‐8.
5
8
1
5
0
3
6
.
9
0
Lime mud, CU
5B
‐06
‐01
2S
16
‐18
8
4
9
4
Sludge/Ash/Lime, CU
5B
‐06
‐02
2
S
3
5
.
5
‐37
.
5
9
4
5
2
Lime/Sludge/Ash, CU
6B
‐16
‐10
1
C
o
m
p
o
s
i
t
e
3
‐50
7
5
‐10
3
5
0
‐74
3
1
2
1
5
Ash/Lime/Sludge, CU
NO
T
E
S
:
1.
1 = Si
r
r
i
n
e
,
19
8
9
;
2 = La
w
,
19
8
2
;
3 = SM
E
,
19
9
5
;
4 = SM
E
,
19
9
9
;
5 = SM
E
,
20
0
6
;
an
d
6 = SM
E
,
20
1
6
.
2.
UU
= Un
c
o
n
s
o
l
i
d
a
t
e
d
Un
d
r
a
i
n
e
d
Co
m
p
r
e
s
s
i
o
n
;
CU
= Co
n
s
o
l
i
d
a
t
e
d
Un
d
r
a
i
n
e
d
Tr
i
a
x
i
a
l
Co
m
p
r
e
s
s
i
o
n
.
Ev
e
r
g
r
e
e
n
Pa
c
k
a
g
i
n
g
,
Ca
n
t
o
n
,
No
r
t
h
Ca
r
o
l
i
n
a
La
n
d
f
i
l
l
6 Ar
e
a
D Ve
r
t
i
c
a
l
In
c
r
e
a
s
e
Su
m
m
a
r
y
of
Wa
s
t
e
Ma
t
e
r
i
a
l
s
Ge
o
t
e
c
h
n
i
c
a
l
Pr
o
p
e
r
t
i
e
s
Co
n
s
i
d
e
r
e
d
in
St
a
b
i
l
i
t
y
An
a
l
y
s
i
s
TA
B
L
E
C ‐1
De
s
c
r
i
p
t
i
o
n
(See Note 2)
Ef
f
e
c
t
i
v
e
St
r
e
s
s
To
t
a
l
St
r
e
s
s
Da
t
a
So
u
r
c
e
(se
e
No
t
e
1 )
Bo
r
i
n
g
ID
S
a
m
p
l
e
ID
De
p
t
h
(f
t
.
be
l
o
w
gr
o
u
n
d
)
To
t
a
l
Un
i
t
We
i
g
h
t
(p
c
f
)
Wa
t
e
r
Co
n
t
e
n
t
(%
)
\\
n
s
e
r
v
e
r
\
C
F
S
\
B
r
p
p
\
N
C
\
V
e
r
t
i
c
a
l
In
c
r
e
a
s
e
\
G
e
o
t
e
c
h
\
M
a
t
e
r
i
a
l
St
r
e
n
g
t
h
s
20
1
6
a
Ta
b
:
T ‐C ‐1 Wa
s
t
e
Pa
g
e
4
of
6
Fr
i
c
t
i
o
n
An
g
l
e
(d
e
g
r
e
e
s
)
Co
h
e
s
i
o
n
(p
s
f
)
Fr
i
c
t
i
o
n
An
g
l
e
(d
e
g
r
e
e
s
)
Co
h
e
s
i
o
n
(p
s
f
)
1A
P
‐18
1
8
.
5
‐23
.
5
1
2
6
1
0
9
1
5
.
9
(
3
)
Compaction Test
1A
P
‐14
2
8
.
5
‐38
.
5
1
3
3
1
1
7
1
4
.
1
(
3
)
Compaction Test
1A
P
‐5
1
8
.
5
‐23
.
5
1
2
7
1
1
2
1
3
.
9
(
3
)
4
0
0
2
0
2
1
6
CU/Compaction Test
1A
P
‐31
4
‐20
1
2
8
1
0
9
1
8
.
6
(
3
)
Compaction Test
1A
P
‐14
2
0
‐35
1
2
7
1
1
0
1
5
.
5
(
3
)
3
2
1
1
5
1
8
.
5
2
0
2
CU/Compaction Test
2B
‐83
‐12
1
2
7
1
0
7
1
7
.
9
(
3
)
Compaction Test
2B
‐10
1
‐8
1
3
1
1
1
3
1
6
.
3
(
3
)
3
2
0
1
9
6
0
0
CU/Compaction Test
2B
‐18
1
‐8
1
2
9
1
1
1
1
6
.
3
(
3
)
3
0
0
1
9
9
0
0
CU/Compaction Test
2B
‐18
1
8
‐23
1
2
7
1
0
8
1
7
.
3
(
3
)
Compaction Test
3
B
9
9
‐10
1
1
0
‐60
1
1
7
14
.
6
3
4
2
6
0
DS
,
ru
n
dry, normal stress > 15 psi
3
B
9
9
‐10
1
1
0
‐60
11
7
14
.
6
38
0
DS
,
ru
n
dry, normal stress < 15 psi
3
B
9
9
‐10
1
1
0
‐60
1
1
7
16
.
4
4
0
0
DS, run wet
4B
‐06
‐04
4
‐14
1
1
9
‐12
4
17
.
8
3
2
1
4
4
DS, run dry
5
NO
T
E
S
:
1.
Da
t
a
So
u
r
c
e
:
1 = Si
r
r
i
n
e
,
19
8
9
;
2 = La
w
,
19
8
2
;
3 = SM
E
,
19
9
9
;
4 = SM
E
,
20
0
6
;
5 = SM
E
,
20
1
6
.
2.
Wi
t
h
th
e
ex
c
e
p
t
i
o
n
of
th
e
di
r
e
c
t
sh
e
a
r
te
s
t
,
to
t
a
l
un
i
t
we
i
g
h
t
is
ma
s
e
d
on
Ma
x
.
dr
y
de
n
s
i
t
y
at
op
t
i
m
u
m
wa
t
e
r
co
n
t
e
n
t
.
3.
Op
t
i
m
u
m
Wa
t
e
r
Co
n
t
e
n
t
,
as
de
t
e
r
m
i
n
e
d
by
St
a
n
d
a
r
d
Pr
o
c
t
o
r
Co
m
p
a
c
t
i
o
n
Te
s
t
i
n
g
.
4.
CU
= Co
n
s
o
l
i
d
a
t
e
d
Un
d
r
a
i
n
e
d
Tr
i
a
x
i
a
l
Co
m
p
r
e
s
s
i
o
n
;
DS
= Di
r
e
c
t
Sh
e
a
r
Te
s
t
.
TA
B
L
E
C ‐2
Su
m
m
a
r
y
of
Pe
r
i
m
e
t
e
r
Di
k
e
Ge
o
t
e
c
h
n
i
c
a
l
Pr
o
p
e
r
t
i
e
s
Co
n
s
i
d
e
r
e
d
in
St
a
b
i
l
i
t
y
An
a
l
y
s
i
s
La
n
d
f
i
l
l
6 Ar
e
a
D Ve
r
t
i
c
a
l
In
c
r
e
a
s
e
Ev
e
r
g
r
e
e
n
Pa
c
k
a
g
i
n
g
,
Ca
n
t
o
n
,
No
r
t
h
Ca
r
o
l
i
n
a
Ef
f
e
c
t
i
v
e
St
r
e
s
s
To
t
a
l
St
r
e
s
s
De
s
c
r
i
p
t
i
o
n
(See Note 4)
To
t
a
l
Un
i
t
We
i
g
h
t
(p
c
f
)
Da
t
a
So
u
r
c
e
(se
e
No
t
e
1 )
Bo
r
i
n
g
ID
De
p
t
h
(f
t
.
be
l
o
w
gr
o
u
n
d
)
Dr
y
De
n
s
i
t
y
(p
c
f
)
Wa
t
e
r
Co
n
t
e
n
t
(%
)
\\
n
s
e
r
v
e
r
\
C
F
S
\
B
r
p
p
\
N
C
\
V
e
r
t
i
c
a
l
In
c
r
e
a
s
e
\
G
e
o
t
e
c
h
\
M
a
t
e
r
i
a
l
St
r
e
n
g
t
h
s
20
1
6
a
Ta
b
:
T ‐C ‐2 Di
k
e
Pa
g
e
5
of
6
Fr
i
c
t
i
o
n
An
g
l
e
(d
e
g
r
e
e
s
)
Co
h
e
s
i
o
n
(p
s
f
)
Fr
i
c
t
i
o
n
An
g
l
e
(d
e
g
r
e
e
s
)
Co
h
e
s
i
o
n
(p
s
f
)
1B
‐89
‐11
1
1
7
1
3
0
1
3
.
2
3
4
2
0
0
2
7
.
5
3
0
0
Undisturbed Sample
1B
‐10
1
3
‐15
1
0
4
1
1
8
1
9
.
7
3
1
.
5
1
0
0
1
6
.
5
4
0
0
Undisturbed Sample
1B
‐11
8
‐11
1
2
4
1
2
5
2
8
.
3
2
8
.
5
6
0
0
1
7
.
5
8
0
0
Undisturbed Sample
NO
T
E
S
:
1.
Da
t
a
So
u
r
c
e
:
1 = La
w
,
19
8
2
.
Ef
f
e
c
t
i
v
e
St
r
e
s
s
To
t
a
l
St
r
e
s
s
Description
TA
B
L
E
C ‐3
Su
m
m
a
r
y
of
Fo
u
n
d
a
t
i
o
n
Ma
t
e
r
i
a
l
Ge
o
t
e
c
h
n
i
c
a
l
Pr
o
p
e
r
t
i
e
s
Co
n
s
i
d
e
r
e
d
in
St
a
b
i
l
i
t
y
An
a
l
y
s
i
s
La
n
d
f
i
l
l
6 Ar
e
a
D Ve
r
t
i
c
a
l
In
c
r
e
a
s
e
Ev
e
r
g
r
e
e
n
Pa
c
k
a
g
i
n
g
,
Ca
n
t
o
n
,
No
r
t
h
Ca
r
o
l
i
n
a
Da
t
a
So
u
r
c
e
(se
e
No
t
e
1 )
Bo
r
i
n
g
ID
De
p
t
h
(f
t
.
be
l
o
w
gr
o
u
n
d
)
To
t
a
l
Un
i
t
We
i
g
h
t
(p
c
f
)
Sa
t
u
r
a
t
e
d
Un
i
t
We
i
g
h
t
(p
c
f
)
Wa
t
e
r
Co
n
t
e
n
t
(%
)
\\
n
s
e
r
v
e
r
\
C
F
S
\
B
r
p
p
\
N
C
\
V
e
r
t
i
c
a
l
In
c
r
e
a
s
e
\
G
e
o
t
e
c
h
\
M
a
t
e
r
i
a
l
St
r
e
n
g
t
h
s
20
1
6
a
Ta
b
:
T ‐C ‐3 Fo
u
n
d
a
t
i
o
n
Pa
g
e
6
of
6
APPENDIX D
STABILITY ANALYSIS
gg
g
Di
r
e
c
t
o
r
y
:
\
\
n
s
e
r
v
e
r
\
C
F
S
\
B
r
p
p
\
N
C
\
V
e
r
t
i
c
a
l
I
n
c
r
e
a
s
e
\
G
e
o
t
e
c
h
\
F
i
l
e
N
a
m
e
:
A
A
6
C
D
V
I
.
g
s
z
Cr
e
a
t
e
d
B
y
:
B
r
i
a
n
B
.
J
o
h
n
s
o
n
,
(
S
e
v
e
e
&
M
a
h
e
r
E
n
g
i
n
e
e
r
s
,
I
n
c
.
)
Me
t
h
o
d
:
B
i
s
h
o
p
,
O
r
d
i
n
a
r
y
a
n
d
J
a
n
b
u
An
a
l
y
s
i
s
N
a
m
e
:
0
2
-
C
-
W
s
t
L
-
R
Co
m
m
e
n
t
s
:
C
r
o
s
s
-
S
e
c
t
i
o
n
A
-
A
'
De
s
c
r
i
p
t
i
o
n
:
C
l
o
s
e
d
,
W
a
s
t
e
,
l
e
f
t
t
o
r
i
g
h
t
s
l
i
p
s
,
s
t
a
t
i
c
.
Me
t
h
o
d
:
B
i
s
h
o
p
,
O
r
d
i
n
a
r
y
a
n
d
J
a
n
b
u
Fa
c
t
o
r
o
f
S
a
f
e
t
y
:
2
.
3
9
Ho
r
z
S
e
i
s
m
i
c
L
o
a
d
:
0
Sl
i
p
s
u
r
f
a
c
e
s
a
r
e
5
f
e
e
t
d
e
e
p
o
r
d
e
e
p
e
r
,
t
o
e
l
i
m
i
n
a
t
e
s
u
r
f
a
c
e
s
l
o
u
g
h
i
n
g
w
h
i
c
h
a
p
p
r
o
x
i
m
a
t
e
s
i
n
f
i
n
i
t
e
s
l
o
p
e
c
o
n
d
i
t
i
o
n
s
(
F
S
=
2
.
5
0
i
n
W
a
s
t
e
f
o
r
t
h
e
4
H
:
1
V
s
l
o
p
e
)
an
d
(
F
S
=
2
.
3
1
i
n
C
o
v
e
r
f
o
r
t
h
e
4
H
:
1
V
S
i
d
e
s
l
o
p
e
)
.
NO
R
T
H
SOUTH
Na
m
e
:
S
o
i
l
C
o
v
e
r
M
o
d
e
l
:
M
o
h
r
-
C
o
u
l
o
m
b
U
n
i
t
W
e
i
g
h
t
:
1
2
5
p
c
f
C
o
h
e
s
i
o
n
:
0
p
s
f
P
h
i
:
3
0
°
P
h
i
-
B
:
0
°
Na
m
e
:
W
a
s
t
e
M
o
d
e
l
:
M
o
h
r
-
C
o
u
l
o
m
b
U
n
i
t
W
e
i
g
h
t
:
9
0
p
c
f
C
o
h
e
s
i
o
n
:
0
p
s
f
P
h
i
:
3
2
°
P
h
i
-
B
:
0
°
Na
m
e
:
P
e
r
i
m
e
t
e
r
D
i
k
e
s
M
o
d
e
l
:
M
o
h
r
-
C
o
u
l
o
m
b
U
n
i
t
W
e
i
g
h
t
:
1
2
0
p
c
f
C
o
h
e
s
i
o
n
:
1
1
5
p
s
f
P
h
i
:
3
2
°
P
h
i
-
B
:
0
°
Na
m
e
:
F
o
u
n
d
a
t
i
o
n
M
a
t
e
r
i
a
l
s
M
o
d
e
l
:
M
o
h
r
-
C
o
u
l
o
m
b
U
n
i
t
W
e
i
g
h
t
:
1
1
5
p
c
f
C
o
h
e
s
i
o
n
:
0
p
s
f
P
h
i
:
3
1
.
5
°
P
h
i
-
B
:
0
°
Na
m
e
:
L
i
n
e
r
M
o
d
e
l
:
M
o
h
r
-
C
o
u
l
o
m
b
U
n
i
t
W
e
i
g
h
t
:
1
2
0
p
c
f
C
o
h
e
s
i
o
n
:
0
p
s
f
P
h
i
:
3
5
°
P
h
i
-
B
:
0
°
Na
m
e
:
B
e
d
r
o
c
k
M
o
d
e
l
:
B
e
d
r
o
c
k
(
I
m
p
e
n
e
t
r
a
b
l
e
)
Di
s
t
a
n
c
e
(
f
t
)
(
x
1
0
0
0
)
0.
0
0
.
2
0
.
4
0
.
6
0
.
8
1
.
0
1
.
2
1
.
4
1
.
6
1
.
8
2
.
0
2
.
2
2
.
4
2
.
6
( 1000)2.352.402.452.502.552.602.652.702.752.802.852.90
(
x
1
0
0
0
)
0.
0
0
.
2
0
.
4
0
.
6
0
.
8
1
.
0
1
.
2
1
.
4
1
.
6
1
.
8
2
.
0
2
.
2
2
.
4
2
.
6
E
l
e
v
a
t
i
o
n
(
f
t
)
(
x
1
0
0
0
)
2.
3
5
2.
4
0
2.
4
5
2.
5
0
2.
5
5
2.
6
0
2.
6
5
2.
7
0
2.
7
5
2.
8
0
2.
8
5
2.
9
0
CF
S
\
B
r
p
p
\
N
C
\
V
e
r
t
i
c
a
l
In
c
r
e
a
s
e
\
G
e
o
t
e
c
h
\
A
p
p
x
D
St
a
b
i
l
i
t
y
Re
s
u
l
t
s
Pa
g
e
1
of
18
00
0
)
1.
4
1
.
6
1
.
8
2
.
0
2
CF
S
\
B
r
p
p
\
N
C
\
V
e
r
t
i
c
a
l
In
c
r
e
a
s
e
\
G
e
o
t
e
c
h
\
A
p
p
x
D
St
a
b
i
l
i
t
y
Re
s
u
l
t
s
Pa
g
e
2
of
18
gg
g
Di
r
e
c
t
o
r
y
:
\
\
n
s
e
r
v
e
r
\
C
F
S
\
B
r
p
p
\
N
C
\
V
e
r
t
i
c
a
l
I
n
c
r
e
a
s
e
\
G
e
o
t
e
c
h
\
F
i
l
e
N
a
m
e
:
A
A
6
C
D
V
I
.
g
s
z
Cr
e
a
t
e
d
B
y
:
B
r
i
a
n
B
.
J
o
h
n
s
o
n
,
(
S
e
v
e
e
&
M
a
h
e
r
E
n
g
i
n
e
e
r
s
,
I
n
c
.
)
Me
t
h
o
d
:
B
i
s
h
o
p
,
O
r
d
i
n
a
r
y
a
n
d
J
a
n
b
u
An
a
l
y
s
i
s
N
a
m
e
:
0
2
-
C
-
W
s
t
L
-
R
-
s
Co
m
m
e
n
t
s
:
C
r
o
s
s
-
S
e
c
t
i
o
n
A
-
A
'
De
s
c
r
i
p
t
i
o
n
:
C
l
o
s
e
d
,
W
a
s
t
e
,
l
e
f
t
t
o
r
i
g
h
t
s
l
i
p
s
,
s
e
i
s
m
i
c
.
Me
t
h
o
d
:
B
i
s
h
o
p
,
O
r
d
i
n
a
r
y
a
n
d
J
a
n
b
u
Fa
c
t
o
r
o
f
S
a
f
e
t
y
:
1
.
5
2
Ho
r
z
S
e
i
s
m
i
c
L
o
a
d
:
0
.
1
3
NO
R
T
H
SOUTH
Na
m
e
:
S
o
i
l
C
o
v
e
r
M
o
d
e
l
:
M
o
h
r
-
C
o
u
l
o
m
b
U
n
i
t
W
e
i
g
h
t
:
1
2
5
p
c
f
C
o
h
e
s
i
o
n
:
0
p
s
f
P
h
i
:
3
0
°
P
h
i
-
B
:
0
°
Na
m
e
:
W
a
s
t
e
M
o
d
e
l
:
M
o
h
r
-
C
o
u
l
o
m
b
U
n
i
t
W
e
i
g
h
t
:
9
0
p
c
f
C
o
h
e
s
i
o
n
:
0
p
s
f
P
h
i
:
3
2
°
P
h
i
-
B
:
0
°
Na
m
e
:
P
e
r
i
m
e
t
e
r
D
i
k
e
s
M
o
d
e
l
:
M
o
h
r
-
C
o
u
l
o
m
b
U
n
i
t
W
e
i
g
h
t
:
1
2
0
p
c
f
C
o
h
e
s
i
o
n
:
1
1
5
p
s
f
P
h
i
:
3
2
°
P
h
i
-
B
:
0
°
Na
m
e
:
F
o
u
n
d
a
t
i
o
n
M
a
t
e
r
i
a
l
s
M
o
d
e
l
:
M
o
h
r
-
C
o
u
l
o
m
b
U
n
i
t
W
e
i
g
h
t
:
1
1
5
p
c
f
C
o
h
e
s
i
o
n
:
0
p
s
f
P
h
i
:
3
1
.
5
°
P
h
i
-
B
:
0
°
Na
m
e
:
L
i
n
e
r
M
o
d
e
l
:
M
o
h
r
-
C
o
u
l
o
m
b
U
n
i
t
W
e
i
g
h
t
:
1
2
0
p
c
f
C
o
h
e
s
i
o
n
:
0
p
s
f
P
h
i
:
3
5
°
P
h
i
-
B
:
0
°
Na
m
e
:
B
e
d
r
o
c
k
M
o
d
e
l
:
B
e
d
r
o
c
k
(
I
m
p
e
n
e
t
r
a
b
l
e
)
Di
s
t
a
n
c
e
(
f
t
)
(
x
1
0
0
0
)
0.
0
0
.
2
0
.
4
0
.
6
0
.
8
1
.
0
1
.
2
1
.
4
1
.
6
1
.
8
2
.
0
2
.
2
2
.
4
2
.
6
( 1000)2.352.402.452.502.552.602.652.702.752.802.852.90
(
x
1
0
0
0
)
0.
0
0
.
2
0
.
4
0
.
6
0
.
8
1
.
0
1
.
2
1
.
4
1
.
6
1
.
8
2
.
0
2
.
2
2
.
4
2
.
6
E
l
e
v
a
t
i
o
n
(
f
t
)
(
x
1
0
0
0
)
2.
3
5
2.
4
0
2.
4
5
2.
5
0
2.
5
5
2.
6
0
2.
6
5
2.
7
0
2.
7
5
2.
8
0
2.
8
5
2.
9
0
CF
S
\
B
r
p
p
\
N
C
\
V
e
r
t
i
c
a
l
In
c
r
e
a
s
e
\
G
e
o
t
e
c
h
\
A
p
p
x
D
St
a
b
i
l
i
t
y
Re
s
u
l
t
s
Pa
g
e
3
of
18
00
0
)
1.
4
1
.
6
1
.
8
2
.
0
2
CF
S
\
B
r
p
p
\
N
C
\
V
e
r
t
i
c
a
l
In
c
r
e
a
s
e
\
G
e
o
t
e
c
h
\
A
p
p
x
D
St
a
b
i
l
i
t
y
Re
s
u
l
t
s
Pa
g
e
4
of
18
gg
g
Di
r
e
c
t
o
r
y
:
\
\
n
s
e
r
v
e
r
\
C
F
S
\
B
r
p
p
\
N
C
\
V
e
r
t
i
c
a
l
I
n
c
r
e
a
s
e
\
G
e
o
t
e
c
h
\
F
i
l
e
N
a
m
e
:
A
A
6
C
D
V
I
.
g
s
z
Cr
e
a
t
e
d
B
y
:
B
r
i
a
n
B
.
J
o
h
n
s
o
n
,
(
S
e
v
e
e
&
M
a
h
e
r
E
n
g
i
n
e
e
r
s
,
I
n
c
.
)
Me
t
h
o
d
:
B
i
s
h
o
p
,
O
r
d
i
n
a
r
y
a
n
d
J
a
n
b
u
An
a
l
y
s
i
s
N
a
m
e
:
0
1
-
O
-
W
s
t
R
-
L
Co
m
m
e
n
t
s
:
C
r
o
s
s
-
S
e
c
t
i
o
n
A
-
A
'
De
s
c
r
i
p
t
i
o
n
:
O
p
e
r
a
t
i
o
n
s
,
W
a
s
t
e
,
r
i
g
h
t
t
o
l
e
f
t
s
l
i
p
s
,
s
t
a
t
i
c
.
Sl
i
p
s
u
r
f
a
c
e
s
a
r
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CF
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14
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Ti
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E ve
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D a t e:
10
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Ti
me
:
12
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:16
PM
Di
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