Performance of a Highway Embankment

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International Conference on Case Histories in

Geotechnical Engineering

Missouri University of Science and Technology

Scholars' Mine

(2004) - Fifth International Conference on Case

Histories in Geotechnical Engineering

Apr 13th - Apr 17th

Performance of a Highway Embankment

Constructed over Landfill Material

Paul J. Lewis

Gannett Fleming, Inc., Camp Hill, Pennsylvania

Jack Mansfield

New Jersey Department of Transportation, Trenton, New Jersey

Syed Ashraf

Gannett Fleming, Inc., South Plainfield, New Jersey

Kessi Zicko

Gannett Fleming, Inc., Camp Hill, Pennsylvania

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Recommended Citation

Paul J. Lewis, Jack Mansfield, Syed Ashraf, and Kessi Zicko, "Performance of a Highway Embankment Constructed over Landfill

Material" (April 13, 2004).

International Conference on Case Histories in Geotechnical Engineering.

Paper 30.

http://scholarsmine.mst.edu/icchge/5icchge/session02/30

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PERFORMANCE OF A HIGHWAY EMBANKMENT

CONSTRUCTED OVER LANDFILL MATERIAL

Paul J. Lewis, P.E.

Gannett Fleming, Inc.

Camp Hill, Pennsylvania -

USA-17011

ABSTRACT

Jack Mansfield, P.E.

New Jersey Dept. of Transportation

Trenton, New Jersey -

USA-08625

Syed Ashraf, P.E.

USA-07080

Gannett Fleming, Inc.

South Plainfield, New Jersey -

Kessi Zicko, E.I.T.

Gannett Fleming, Inc.

Camp Hill, Pennsylvania -

USA-17011

This paper presents settlement data over a period of 12 years for two portions of a highway embankment constructed over landfill material. Construction was completed in 1989 and included dynamic compaction to limit post construction settlement. A preload / surcharge was used over a separate portion of one of the highway embankments as an alternative foundation improvement technique for the purpose of comparison and evaluation of the effectiveness of the two methods. Elevation measurements taken over a period of

12 years are presented for comparison of post construction settlement of both dynamically compacted and surcharged sections of the highway embankments.

INTRODUCTION

The interchange of New Jersey Route 18 with the Garden

State Parkway was constructed in 1988. The alignments of the mainline roadways and connector ramps associated with this interchange traverse the former Tinton Falls Landfill. This municipal landfill ceased operation in the early 1970’s.

Dynamic compaction was used to densify the landfill prior to constructing the highway embankments in order to limit postconstruction settlement. For comparison to dynamic compaction, a preload / surcharge embankment was used over a portion of one embankment as an alternative soil improvement technique. Elevation measurements taken over a period of twelve years following completion of construction provide a comparison of the effectiveness of the two ground improvement techniques. The purpose of this paper is to present the elevation data collected over the twelve years following completion of construction and provide an evaluation of the effectiveness of dynamic compaction versus surcharging / preloading in limiting long term settlement of a highway embankment constructed over a municipal landfill.

An evaluation and comparison of the monitored secondary compression settlements are presented. A brief description of the project site conditions, dynamic compaction process and surcharge / preload construction are presented herein. A more detailed description of the project can be found in Lewis and

Langer [1994]. A plan view of the project site showing the monitoring sections and the approximate limits of the landfill is presented in Fig. 1.

SITE CONDITIONS

The project grades and alignment required construction of highway embankments ranging from 3 to 9 meters in height over the landfill. The landfill material generally consists of domestic sanitary refuse with occasional deposits of organic refuse (yard waste) and construction debris. In general, the landfill material was estimated to consist of approximately

45 percent organic material. The typical depth of the landfill material varied from about 1.8 to 7.4 meters. The landfill is underlain by coastal plain deposits consisting primarily of medium dense to dense silty sand. Groundwater is located at the bottom of the landfill.

DYNAMIC COMPACTION

Dynamic compaction completed on this site consisted of highenergy drops with an 18,160-kilogram weight dropped from a height of 24.4 meters. Two solid steel weights with different cross sections were used for high-energy drops. One consisted of a 1.8-meter square weight while the other consisted of a

2.1-meter diameter circular weight. The weight was dropped five to ten times at each location until maximum compaction was achieved as evidenced by no increase in crater depth.

Dynamic compaction was completed on a square grid pattern with a final grid spacing of 3.8 meters center to center.

Craters produced from high-energy impacts were backfilled with granular material which was subsequently compacted with a low-energy ironing pass performed with an

18,160-kilogram weight dropped from a height of 12.2 meters.

Paper No. 2.51 1

Fig.1 Plan view of the project site showing the station limits of dynamic compaction and preload / surcharge ground improvements.

The low-energy weight consisted of a 5.8-meter square weight constructed of solid steel. The ironing pass utilized an overlapping grid pattern.

SURCHARGE / PRELOAD

A portion of one of the interchange ramps (Ramp E) was selected to receive a preload / surcharge in lieu of dynamic compaction. A 1.5-meters high surcharge was constructed over the final profile grade and the embankment was monitored for a period of 6 months. At the end of the 6-month preload period, the surcharge was removed and final roadway construction was completed.

MONITORING

Following completion of construction, portions of the roadway embankment were monitored by periodic elevation surveys.

Elevation measurements were collected along Route 18 SW at

100-foot intervals from station 1394+00 to station 1399+00 where the underlying landfill material was compacted by the dynamic compaction process. Elevation measurements were also collected along Ramp E at 100-foot intervals from station

13+00 to station 19+00 where the underlying landfill material was treated by preloading / surcharging. Survey elevation data were collected over a period of twelve years. Comparing the periodic survey elevation data to the as-built roadway elevations allows for the computation of settlement with time.

Tables 1 and 2 present the embankment height, landfill thickness, and total settlement observed over the monitoring period at each location monitored for the roadway embankment underlain by landfill treated by dynamic compaction and preload / surcharge, respectively.

EVALUATION OF LONG TERM PERFORMANCE

Analysis of the data presented in Tables 1and 2 indicates that the total settlement observed over the monitoring period for the embankment underlain by landfill treated by dynamic compaction ranges from approximately 85 to 215 mm. Total settlement observed for the same period for the embankment underlain by landfill treated by preload / surcharge ranges from approximately 282 to 651 mm. Tables 3 and 4 present the ratio of total settlement in mm to landfill thickness in meters in order to compare the total settlement based on an equivalent thickness of landfill material. From Table 3, the observed settlement for the area treated by dynamic compaction ranged from 24.3 to 48.3 and averaged 36.9 mm of settlement per meter of landfill thickness over the 12-year monitoring period. In comparison, from Table 4, the observed settlement for the area treated by preload / surcharge ranged from 47.8 to 89.2 and averaged 72.4 mm of settlement per meter of landfill thickness over the 12-year monitoring period.

Paper No. 2.51 2

Table 1. Dynamic Compaction Summary

Station

1394+00

1395+00

Embankment

Height

(m)

8.3

7.7

Landfill

Thickness

(m)

2.3

1.8

Sep-91

46

9

1396+00

1397+00

1398+00

1399+00

5.4

4.5

3.0

3.3

3.5

4.6

6.7

6.5

Note: Construction of embankment completed in 1989.

Table 2. Preload / Surcharge Summary

58

24

33

Station

13+00

14+00

15+00

Embankment

Height

(m)

7.5

6.7

5.2

Landfill

Thickness

(m)

6.2

6.3

7.1

Sep-91

55

186

167

16+00

17+00

18+00

19+00

4.0

3.2

2.7

2.3

7.4

7.3

6.6

5.9

217

147

25

18

Note: Construction of embankment completed in 1989.

Table 3. Ratio of Total Settlement to Landfill Thickness for

Dynamic Compaction Area

Station

Landfill

Thickness

(m)

Total

Settlement

(mm)

Ratio of Total

Settlement to

Landfill

Thickness

(mm/m)

1394+00

1395+00

1396+00

1397+00

1398+00

1399+00

2.3

1.8

3.5

4.6

6.7

6.5

114

87

85

149

215

-

49.6

48.3

24.3

32.4

32.1

-

Range = 24.3 to 49.6 mm/m

Average = 37.3 mm/m

Jul-93

40

24

30

79

58

55

Settlement

(mm)

Apr-95 Sep-97

48

17

1

62

75

62

66

36

23

85

116

93

Feb-00

51

25

13

77

126

Mar-03

114

87

85

149

215

Jul-93

43

213

183

241

180

34

Settlement

(mm)

Apr-95 Sep-97

179

321

325

228

378

397

387

308

147

100

464

426

214

144

Feb-00

261

414

441

508

497

256

168

Mar-03

375

536

564

636

651

389

282

Table 4. Ratio of Total Settlement to Landfill Thickness for

Preload / Surcharge Area

Station

Landfill

Thickness

(m)

Total

Settlement

(mm)

Ratio of Total

Settlement to

Landfill

Thickness

(mm/m)

13+00

14+00

15+00

16+00

6.2

6.3

7.1

7.4

375

536

564

636

60.5

85.1

79.4

85.9

17+00

18+00

19+00

7.3

6.6

5.9

651

389

282

Average =

89.2

58.9

47.8

Range = 47.8 to 89.2 mm/m

72.4 mm/m

Paper No. 2.51 3

Figure 2 presents a settlement profile vs. time for the embankment underlain by landfill treated by dynamic compaction while Fig. 3 presents a settlement profile vs. time for the embankment underlain by landfill and treated by preload / surcharge. Review of Figures 2 and 3 indicate that

-800

-600

-400

Embankment

Height

-200

0

200

400 the roadway embankment constructed over landfill material treated by dynamic compaction is performing well with respect to observed settlement over the 12-year monitoring period as compared to the roadway embankment constructed over landfill material treated by preload / surcharge.

16

12

8

1989

2003

Landfill

Thickness

4

0

-4

-8

1989

1991

1993

1995

1997

2000

2003

600 -12

800

1393 1394 1395 1396 1397 1398 1399 1400

-16

Station (+00)

Fig. 2. Settlement profile along portion of mainline embankment subjected to dynamic compaction.

-800

-600

-400

-200

Embankment

Height

16

12

8

0

200

400

600

Landfill

Thickness

1989

2003

4

0

-4

-8

-12

1989

1991

1993

1995

1997

2000

2003

800

12 13 14 15 16

Station (+00)

17 18 19 20

-16

Fig. 3. Settlement profile along portion of Ramp E embankment subjected to preload / surcharge.

Paper No. 2.51 4

Secondary settlement in the dynamic compaction area is progressing at a much slower rate and differential settlement is not as extreme as that observed in the preload / surcharge area.

Figures 4 and 5 present photographic representation of the roadway performance for each of the sections monitored.

Fig. 4. Minimal deformation of the roadway occurred due to settlement at the Dynamic Compaction location.

Fig. 5. Significant deformation of the roadway was caused by settlement at the Ramp E Preload / Surcharge location.

Figure 6 presents total settlement vs. time for all monitored locations for both the dynamic compaction and preload / surcharge treatment areas. As shown in this figure, dynamic compaction was more effective in reducing the rate of secondary settlement as compared to the preload / surcharge treated area. In order to compare and quantify the reduction in the rate of secondary settlement, the coefficient of secondary compression (C

Paper No. 2.51

α

) was computed from total settlement vs. time data collected for each monitoring point. The following equation from Bowles [1984] was used to perform the back calculation assuming that primary compression was complete in 1991:

= ∆ε / Log (t

2

/t

1

) C

α

(1)

Tables 5 and 6 present the computed coefficient of secondary compression for each monitoring location. Review of Table 5 indicates that C

α

ranges from 0.0153 to 0.0513 with an average value of 0.0313 for the landfill material treated by dynamic compaction. Review of Table 6 indicates that C

α ranges from 0.0529 to 0.0817 with an average value of 0.0657 for the landfill material treated by preload / surcharge.

NAVFAC [1982] indicates that the coefficient of secondary compression for landfills which have experienced decomposition for 10 to 15 years prior to new loading ranges from 0.02 to 0.07. For the landfill materials subjected to dynamic compaction, the C

α

values are generally in the lower portion of this range. The C

α

values for the landfill materials that underwent the preload / surcharge soil improvement are in the upper portion of the range.

CONCLUSION

Review of settlement data collected over a period of 12 years after construction of a highway embankment built over landfill material treated using two different ground modification techniques indicates that dynamic compaction is more effective in reducing the rate of secondary compression than preload / surcharging. The settlement observed over the

12-year period per meter of landfill thickness is approximately double in the preload / surcharge area as compared to the area treated by dynamic compaction. Furthermore, back calculation of the coefficient of secondary compression indicates that this parameter was effectively reduced by up to

50 percent for landfill material treated by dynamic compaction as compared to landfill material treated by preload / surcharging.

REFERENCES

Bowles, J.E. [1984]. “Physical and Geotechnical Properties of Soils”, McGraw-Hill Book Company, New York, NY.

Lewis, P.J. and J.A. Langer [1994]. “Dynamic Compaction of

Landfill Beneath Embankment”, ASCE Geotechnical Special

Publication No. 40: Vertical and Horizontal Deformations of

Foundations and Embankments , pp. 451-461.

U.S. Department of the Navy [1983]. “ Soil Dynamics, Deep

Stabilization, and Special Geotechnical Construction”, Design

Manual 7.3, NAVFAC DM7.3, Naval Facilities Engineering

Command, Alexandria, VA.

5

0

100

200

300

400

500

600

700

Solid Lines - Preload / Surcharge

Dashed Lines - Dynamic Compaction

13+00

14+00

15+00

16+00

17+00

18+00

19+00

1394+00

1395+00

1396+00

1397+00

1398+00

1399+00

800

1988 1990 1992 1994 1996 1998 2000 2002 2004

Year

Fig. 6. Comparison of the amount settlement of embankments at the Dynamic Compaction and Preload / Surcharge locations.

Table 5. Coefficient of Secondary Compression (C

α

) of Landfill Material at the Dynamic Compaction Area

Station

Landfill Thickness

(m)

Settlement (mm)

Sep-91 Mar-03 C

α

1394+00

1395+00

1396+00

1397+00

1398+00

1399+00

2.3

1.8

3.5

4.6

6.7

6.5

46

9

30 (a)

58

24

33

114

87

85

149

215

93 (b)

0.0350

0.0513

0.0289

0.0234

0.0337

0.0153

(a) Jul-93 data point

(b) Sep-97 data point

Range = 0.0153 to 0.0513

Average =

Table 6. Coefficient of Secondary Compression (C

α

) of Landfill Material at the Preload / Surcharge Area

0.0313

Station

13+00

14+00

15+00

Landfill Thickness

(m)

6.2

6.3

7.1

Settlement (mm)

Sep-91 Mar-03

55

186

167

375

536

564

C

α

0.0611

0.0657

0.0662

16+00

17+00

18+00

19+00

7.4

7.3

6.6

5.9

217

147

25

18

636

651

389

282

0.0670

0.0817

0.0653

0.0529

Range = 0.0529 to 0.0817

Average = 0.0657

Paper No. 2.51 6

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