16. 00-31-32_1-3-C_20081222_Geotech_Canutillo_Final_VI_S&B.pdf
PDF 22 MB Posted
- Attached to
- Sunland Park Levee Rehabilitation
- Solicitation number
- 191BWC22R0002
View the file
Other files
Show all 50
On GovTribe
Work with this file
- Download the original file
- Contacts named in this file
- Similar government files
- Ask GovTribe AI about this file
Text version
FINAL
TECHNICAL MEMORANDUM
VOLUME I
FOR
Geotechnical Explorations of Levee System Within the Rio Grande Canalization Project
CANUTILLO LEVEE SEGMENT
Prepared for:
United States Section, International Boundary & Water Commission
Submitted / Prepared by:
Project Manager: Daniel O. Rios Deputy Project Manager: Sharlotte L. Teague Task Order Manager: James Sassin, PE
In Association With:
Raba-Kistner Consultants, Inc.
Contract No. IBM05D0001 Task Order No. IBM08T0009 December 22, 2008
XX
XX
FINAL TECHNICAL MEMORANDUM
Geotechnical Explorations of Levee System Within the Rio Grande Canalization Project
Contract No. IBM05D0001 Order No. IBM08T0009 i
ACKNOWLEDGEMENT / CERTIFICATION
The preparation of this document included the collaborative participation of the following parties:
US Section, International Boundary & Water Commission
• Colleen Jaye Elliott Contracting Officer El Paso
• Josè A. Nuñez, PE Principal Engineer El Paso
• Steve Lyell Technical Manager El Paso
Contractor Team
• Daniel O. Rios Project Manager S&B, McAllen
• Sharlotte L. Teague Deputy Project Manager S&B, McAllen
• James Sassin, PE Task Order Manager S&B, Austin
• Chris L. Schultz Project Manager (Geotech) R-K, San Antonio
• John A. Focht III Chief Geotechnical Engineer R-K, San Antonio
• John Cordova, PE Project Engineer R-K, El Paso
• Jerrell “Bo” Blackmon GIS Manager S&B, McAllen
• Victor Pena Engineering Assistant S&B, McAllen
• Hazel Herrera Lead GIS Technician S&B, McAllen
All geotechnical sampling, testing, evaluations, and analysis for this Technical Memorandum were developed under a geotechnical study by Rabal-Kistner Consultants, Inc. entitled, “Geotechnical Exploration and Engineering Evaluation of Levee System The Rio Grande Canalization Project - Canutillo Segment Revised Final Technical Memorandum, December 22, 2008”.
ii
This Page Intentionally Blank iii
TABLE OF CONTENTS
VOLUME I: Page
SECTION 1 PURPOSE OF TECHNICAL MEMORANDUM
1.1 Introduction / Background ……………………………………… 1 -1
1.2 Project Description ………………..………………….…………. 1 -1
1.3 Scope of Work ………………..…………………………………. 1 -2
1.4 Records / References / Acronyms……………………..………… 1 -4
SECTION 2 GEOTECHNICAL EXPLORATION / EVALUATION
2.1 Levee Segment Description……………………….……………… 2 -1
2.2 Previous Geotechnical Studies……..………………….…………. 2 -1
2.3 Risk …………………………………..………………….…………. 2 -4
2.4 Limitations…………………………..………………….…………. 2 -5
2.5 Field Exploration……………………..………………….…………. 2 -6
2.6 Laboratory Testing……………..…………………………………. 2 -7
2.7 General Site Conditions……………………..…………..………… 2 -9
2.8 Impact of Sampling / Testing Procedures on Measured and
Design Soil Properties………………..………………….…………. 2 -12
2.9 Design Considerations – Earthen Levee System……..………… 2 -14
2.10 Slope Stability – Earthen Levee System…..…………..………… 2 -17
2.11 Seepage Analysis– Earthen Levee System…..…………..………… 2 -22
2.12 Erosion Protection– Earthen Levee System…..…………..……… 2 -25
2.13 Design Considerations – Flood Wall System…..………..……… 2 -26
2.14 Stability – Flood Wall System…..………………………....……… 2 -27
2.15 Seepage Analysis – Flood Wall System…..………..………..…… 2 -29
2.16 Settlement Associated with the Proposed Raised Levee………… 2 -29
2.17 Settlement Associated with the Flood Wall System……………… 2 -30
2.18 Earthquake Induced Deformation………………………...……… 2 -30
2.19 Trafficability……………………………...…..…………..………… 2 -32
2.20 Conclusions…………………….……………..…………..………… 2 -32
2.21 Recommendations…………….……………..…………..………… 2 -32
2.22 Notes / Bibliography……………….…….…..…………..………… 2 -38
SECTION 3 GIS PROJECT DATABASE
3.1 Inventory …………………………….…..………………………… 3 -1
3.2 Survey & Mapping………..…………….……………….…………. 3 -2
3.3 Three-Dimensional Geographic Information System Model……. 3 -2 iv
TABLES:
Page Table 1-1 Definitions / Acronyms……………..………………….…………. 1 -4
Table 2-0 Canutillo Segment Condition Assessment by USACE…. 2 -2 Table 2-1 Canutillo Levee Segment, Samples Collected.……… ….…. 2 -7
Table 2-2 Canutillo Levee Segment, Laboratory Tests.………… ….. 2 -8 Table 2-3 Canutillo Levee Segment, Direct Shear Test Results…….. 2 -8 Table 2-5 Required Factors of Safety…………………………………………. 2 -17 Table 2-6 Soil Parameters………………………………………………………. 2 -20 Table 2-7 Computed Factors of Safety…………………………………… 2 -20 ~ 22
Table 2-8 Summary of Steady-State Seepage Analysis …………………. 2 -24 Table 2-9 Maintenance Roadway Base Gradation ………………………. 2 -38
FIGURES:
Page Figure 2-1 Canutillo Levee Segment, Hydraulic Conductivity Test Results…. 2 -9
Figure 2-2 Assumed Geometries of Steady-State Seepage Analysis..……. 2 -23 Figure 2-3 Remedial Repair Option 1…………………………………....……. 2 -33
Figure 2-4 Remedial Repair Option 2…………………………………....……. 2 -33 Figure 2-5 Reconstruction Option ……………………………………....……. 2 -34
APPENDIX A FIELD DATA
A.1 Bore Coordinates & Elevations A.2 Logs of Borings A.3 Key to Terms & Symbols A.4 Results of Soil Sample Analyses
VOLUME II:
APPENDIX A FIELD DATA, continued.
A.5 Field Photos
APPENDIX B LABORATORY TEST REPORTS
B.1 Grain Size Distribution B.2 Consolidated Drained Triaxial Compression – N/A B.3 Hydraulic Conductivity (Permeability) Test Reports B.4 Direct Shear Test Reports v
APPENDIX C SLOPE STABILITY, ANALYSES, AND RESULTS
APPENDIX D EXISTING CROSS-SECTIONS
APPENDIX E DESIGN CROSS-SECTIONS
APPENDIX F REVISED EMBANKMENT MATERIAL SPECIFICATION
APPENDIX G OPINION OF PROBABLE COST / BACK-UP DATA
EXHIBIT I BORE LOCATION MAPS
(Separate Cover)
EXHIBIT II DIGITAL ELEVATION MAPS
(Separate Cover) vi
SECTION 1 -1
1.0 PURPOSE OF STUDY
1.1 Introduction / Background
The United States Section of the International Boundary and Water Commission (USIBWC) conducted hydraulic and aerial geophysical studies of the Rio Grande Canalization Project to assess the ability of the associated levees to safely contain flood flows in the Rio Grande:
“Condition Assessment of U.S. International Boundary & Water Commission, Texas and New Mexico Levees” by the US Army Corps of Engineers (USACE) dated June 2004, and the “Flood Simulation Study of Rio Grande Levees Near Las Cruces, New Mexico, Using Seismic and Electrical Geophysical Methods” dated May 2007. From these studies, the USIBWC determined that certain reaches of the levees require rehabilitation improvements in order to meet Federal Emergency Management Agency (FEMA) requirements for the safe containment of 100-year flood flows.
The Rio Grande Canalization Project was completed in 1943 pursuant to Public Resolution No. 4- 74th Congress, Approved February 13, 1935, Control and Canalization of the Rio Grande- Caballo Dam, New Mexico to El Paso, Texas. The Project extends for 105.6 miles along the Rio Grande from Percha Dam to the American Dam at El Paso. The Rio Grande Canalization Project consists of a normal flow channel and a leveed floodway. The normal channel carries the irrigation releases from Elephant Butte and Caballo Dams to the headworks of irrigation projects developed by the US Bureau of Reclamation in New Mexico and Texas and also carries waters released for delivery to Mexico under the Treaty of 1906. The normal flow channel has a depth of 3 to 5 feet, a width ranging from 110 to 500 feet, and a capacity of 2,500 cubic feet per second (cfs) above Leasburg Dam to 1,200 cfs at El Paso. The floodway varies from about 50 to 2,100 feet in width.
Its bordering levees are 3 to 15 feet in height and have a total length of 130 miles. The crowns of the levees are gravel surfaced to facilitate access during flood emergencies and maintenance.
Some of the floodway lands are used for recreational purposes and the remainder largely for grazing and agriculture.
On February 13, 2008 a unilateral task order was issued by the USIBWC to S&B Infrastructure, Ltd. (S&B), as Contractor, to prepare a technical memorandum for geotechnical explorations and analysis of the existing levee system within the Rio Grande Canalization Project. S&B subcontracted the geotechnical exploration, laboratory testing, and evaluations to Raba-Kistner Consultants, Inc. The following information, along with a Borehole Location Map under separate cover, comprises the Technical Memorandum – Geotechnical Explorations of Levee System within the Rio Grande Canalization Project for the Canutillo Levee Segment.
1.2 Project Description: Canutillo Levee Segment
The Canutillo Levee Segment of the Rio Grande Canalization Project is approximately 31 miles in length (from River Mile 1 to River Mile 32) along the Rio Grande in Dona Ana County, New Mexico and El Paso County, Texas. (Although the majority of this segment is proposed to be earthern levee, there is a planned flood wall portion of the east alignment that extends from about Mile 10.85 to about Mile 13.5.) The average existing height of the east and west levee of the
SECTION 1 -2
Canutillo Levee Segment is approximately 5.2 feet. As a result of the previously referenced studies mentioned in Section 1.1, paragraph 1, and the determinations made by the USIBWC, it is also understood that the proposed levee will remain at its existing height in some areas, and up to
10.27 feet may be added in other areas of the alignment. For a majority of this section, additional heights of 3.5 feet or less are anticipated.
1.3 Scope of Work
The work to be performed included geotechnical investigations and evaluations along the alignment of the levee reach. Field work was coordinated with the USIBWC American Dam and Las Cruces Field Offices. The technical memorandum contains the findings of the geotechnical investigations and evaluations, and also includes a set of location maps (24 inch x 36 inch, scale1 inch = 1,000 feet) under separate cover.
The Contractor provided personnel and equipment necessary to perform geotechnical investigations and engineering evaluations, incorporating existing geotechnical studies provided by the USIBWC, and took into account slope stability, levee settlement, through-seepage, under-seepage, and trafficability of levees located in and around the Canutillo Levee Segment of the Rio Grande Canalization Project. The engineering evaluations conform to current engineering practices as defined by the US Army Corps of Engineers Engineering Manual 1110-2-1913, Design and Construction of Levees and 44 CFR 65.10. All samples were classified and recorded using standard reporting procedures.
Specific activities and requirements that were performed by the Contractor included the following:
1.3.1 Site Exploration – Borings.
1.3.1(a) The proposed boring locations were identified on project maps and submitted to the USIBWC for review prior to mobilization to the site. The boring spacings are approximately 1000 linear feet intervals. The Contractor provided recommendations with regards to other areas where additional borings were required to address associated previous meanders or areas of known highly variable soils identified by previous studies.
1.3.1(b) The borings were located and staked in the field by an engineer and geologist prior to drilling utilizing tape and right angle measurements from existing benchmarks.
Final boring locations were surveyed in the field by the USIBWC, and are included in Appendix A-1. Screening of locations were coordinated with the American Dam and Las Cruces USIBWC Field Offices.
1.3.1(c) The field drilling included borings at a spacing of no more than 1000 linear feet, altering the spacing where required to drill in identified anomalies discovered during the geophysical study and in areas defined by the Contractor. The spacing of borings were not arbitrarily uniform but rather based upon available geologic information. Boring depths were deep enough to provide data for stability analyses of
SECTION 1 -3
the levee and foundation (at least equal to the height of proposed levee at its highest point but not less than 10 feet with distinctions made between borings for the preliminary stage and final-design stage). The boring depths identified below were based on a levee height of 7.5 feet or less combined with the additional height to be added identified in the USIBWC documents, taken to the next 5-foot increment. If auger refusal was encountered in these borings prior to achieving their intended depths, the borings would be terminated 10 feet into rock. The following outlines the depths and total linear footage of drilling for the Canutillo Levee Segment:
• Average Height of East Levee (Rail) = 5.2 feet
• Average Height of West Levee = 5.2 feet
• Number of borings = 266
• Depth of Bores = 20 feet to 150 feet
1.3.1(d) All drilling activities were logged by the Contractor to include samples taken, major stratum changes, and general conditions of drilling and any unusual aspects of the boring location or drilling and sampling procedures.
1.3.1(e) Where auger refusal wass encountered, air-rotary and/or mud-rotary drilling techniques were utilized to advance the borings to their final depths, and grab samples were collected from the cuttings. Representative portions of all samples were sealed and packaged for transportation to the Contractor’s laboratory.
1.3.1(f) Standard geotechnical drilling techniques were utilized for all borings. The borings were backfilled utilizing bentonite grout. No containerizing and/or off-site disposal of the soil cuttings were required.
1.3.1(g) In all test borings, ground water level readings were taken upon completion of drilling activities, and the borings were backfilled in accordance with USIBWC’s Realty Office requirements.
1.3.2 Site Exploration – Soil Sampling.
1.3.2(a) All soil borings were sampled at 2.5-foot intervals in the first 5 feet, and at 5-foot intervals thereafter.
1.3.2(b) In sandy soils, Standard Penetration Test samples were collected. In cohesive soils, sampling was alternated between Shelby tube and Standard Penetration Test samples.
1.3.3 Site Exploration – Laboratory Testing.
1.3.3(a) In each boring, standard strength and classification testing were performed:
moisture content tests, Atterberg Limits (plasticity tests), gradation, and unconfined
SECTION 1 -4
compression tests. In addition to the standard testing program, the following tests were performed on the basis of conditions encountered in the field:
• Consolidation Test = 1 per 4 miles (anticipating predominately sandy soils).
• Permeability Test = 1 per mile
• Double Hydrometer Test (dispersivity) = 1 per 2 miles
• Moisture Density Test = 1 per five miles
• Direct Shear or Consolidated-Drained Triaxials = 1 per 5 miles
1.3.3(b) All samples were classified and recorded using standard reporting procedures.
1.3.4 GIS Inventory, Database, and Mapping.
The Contractor developed a Geographic Information System (GIS) project inventory and database, as well as a three-dimensional (3D) model in both Environmental Systems Research Institute (ESRI) GIS format and AutoCAD Civil 3D 2008 format which captures all levee elevation information as well as soil boring locations and depths. The Contractor also produced location and analysis maps. A site visit was also performed where photographs and data was collected regarding physical features (cross-drainage structures, access roads, etc.) of the Canutillo Levee Segment.
1.4 References and Definition of Acronyms
The following records and information were provided by the USIBWC and reviewed by the Contractor as background information:
• The USACE report “Condition Assessment of U.S. International Boundary & Water
Commission, Texas and New Mexico Levees” dated June 2004, with associated GIS, pdf, and other files.
• The report “Flood Simulation Study of Rio Grande Levees Near Las Cruces, New
Mexico, Using Seismic and Electrical Geophysical Methods” dated May 2007.
• Water surface profile for 100-year flood fully contained.
• Technical Memorandum: Conceptual Design Study of Replacement Canal Lining American Canal, American Dam to International Dam, Oct 2001.
• Environmental “Final Assessment, Flood Control Improvements to the Rio Grande
Canalization Project,” dated December 2007.
• Lidar Data.
• “Technica l Memorandum: Environmental Issues and Concerns, Conceptual Design Study of Replacement Canal Lining, American Canal, American Dam to International Dam,” Prepared for the USIBWC by Montgomery Watson Harza, June 7, 2002.
SECTION 1 -5
• “Analysis of Contamination on the USIBWC Property in Relation to the ASARCO El
Paso Smelter,” prepared by Allen J. Medine, July 27, 2007.
• Old River Meander Schedule
Although some acronyms have been defined above, Table 1-1 below provides a consolidated summary of terms used throughout this Technical Memorandum.
Acronym Definition
3D three-dimensional CD consolidated drained CU consolidated undrained cfs cubic feet per second DEM Digital Elevation Model DLG Digital Line Graph EPA Environmental Protection Agency ERDC Engineer Research and Development Center ESRI Environmental Systems Research Institute FEMA Federal Emergency Management Agency GIS Geographic Information System (H:V) Slope, horizontal to vertical Hz Hertz IBC International Building Code kHz Kilohertz (1,000 Hertz) NED National Elevation Datasets R-K Raba-Kistner Consultants, Inc.
S&B S&B Infrastructure, Ltd.
SCAPS Site Characterization and Analysis Penetrometer System SPT Standard Penetration Tests TDS Total Dissolved Solids TxDOT Texas Department of Transportation USCS Unified Soil Classification System USIBWC United States Section, International Boundary and Water Commission USACE US Army Corps of Engineers USACE EM US Army Corps of Engineers Engineering Manual
Table 1-1: Definition of Terms
SECTION 1 -6
SECTION 2 -1
2.0 GEOTECHNICAL EXPLORATION / EVALUATION
Raba-Kistner Consultants, Inc. (R-K) completed the authorized subsurface exploration and engineering analyses of the Canutillo Levee Segment of the Rio Grande Canalization Project located in south central New Mexico. The following briefly describes the procedures utilized during this study and presents R-K’s findings along with their geotechnical analyses of the levee which was performed in general accordance with the US Army Corps of Engineers (USACE) Engineering Manual (EM) 1110-2-1913 Design and Construction of Levees as it pertains to geotechnical evaluations.
2.1 Levee Segment Description
The Canutillo Levee Segment of the Rio Grande Canalization Project consists of approximately 32 miles of existing levees, all of which run parallel to the Rio Grande in New Mexico and in El Paso County, Texas.
On the basis of information provided by the USIBWC, it is understood that the average existing height of the east and west levee of the Canutillo Levee Segment is approximately 5.2 feet. As a result of the previously referenced studies mentioned in Section 1.1, paragraph 1, and the determinations made by the USIBWC, it is also understood that the proposed levee will remain at its existing height in some areas, and up to 10.27 feet may be added in other areas of the alignment. For a majority of this section, additional heights of 3.5 feet or less are anticipated.
The majority of this segment exists as, and is proposed to be, an earthern levee; however, there is a planned flood wall portion of the East alignment that extends from about Mile 10.85 to about Mile
13.5. The flood wall is planned to have a top-of-wall elevation ranging from about EL +3,768 ft to EL +3,772.75 ft, representing a free-board of 3 ft with respect to the 100 year design flood stage elevation, and a height of about 2.25 to 5.8 ft above the existing top of levee. The raised earthen levee will also provide a minimum free-board of 3 feet with respect to the design flood stage. All stability and seepage calculations are based on this 3-foot assumption
2.2 Previous Geotechnical Studies
The USACE Engineer Research and Development Center (ERDC) in Vicksburg, MS performed a condition assessment1 in 2004 of a portion of the levees along the Rio Grande in Texas and New Mexico. This document (USACE ERDC-TR-03-04) included the results of geophysical testing of the Canutillo Levee Segment; the document also subdivided the levee segment by quadrangle (Smeltertown, Canutillo, La Union, and La Mesa, and further subdivided the Canutillo Levee Segment into major twenty (2) subsections identified as SMELT-01, SMELT-02, SMELT-03, SMELT-04, SMELT-05, SMELT-06, CANUT-01, CANUT-02, CANUT-03, CANUT-04, CANUT-05, CANUT-06, LAUNI-01, LAUNI-01, LAMES-01, LAMES-02, LAMES-03, LAMES-04, LAMES-05, and LAMES-06, and outlined (in Table 2.2), the values and overall scores for the levee condition assessment for each subsection. An excerpt of this table is shown in Table 2-0 on the next two pages.
SECTION 2 -2
Table 2-0: Canutillo Levee Segment Condition Assessment by USACE1
Segment ID Quad
Perfor-mance
Constr History
Visual Insp
Mat’l Type
Topo Irreg
Slope Stab
Man Inrt Geology
Borrow Areas Anom SCORE
Avg Score
Condition Assessment
SMELT-
01 Smeltertown 2.0 2.0 2.0 1.5 0.0 1.0 4.0 2.0 4.0 4.0 59.5 5.95 Marginal
SMELT -
02 Smeltertown 2.0 2.0 2.0 1.0 3.0 1.0 4.0 1.0 3.0 4.0 62.0 6.20 Marginal
SMELT -
03 Smeltertown 2.0 2.0 2.0 1.5 2.0 1.0 3.0 2.0 4.0 4.0 62.5 6.25 Marginal
SMELT -
04 Smeltertown 2.0 2.0 2.0 1.0 2.0 0.5 3.0 1.0 4.0 4.0 56.5 5.65 Marginal
SMELT -
05 Smeltertown 2.0 2.0 2.0 1.0 1.0 0.5 3.0 1.0 4.0 4.0 53.5 5.35 Marginal
SMELT -
06 Smeltertown 2.0 2.0 2.0 1.5 0.0 1.0 4.0 2.0 4.0 4.0 59.5 5.95 Marginal
CANUT-
01 Canutillo 2.0 2.0 2.0 0.5 2.0 0.5 4.0 1.0 3.0 4.0 56.0 5.60 Marginal
CANUT -
02 Canutillo 2.0 2.0 2.0 0.5 0.0 0.0 3.0 0.5 4.0 4.0 46.0 4.60 Marginal
CANUT -
03 Canutillo 2.0 2.0 2.0 0.5 3.0 1.0 3.0 0.5 4.0 4.0 58.0 5.80 Marginal
CANUT -
04 Canutillo 2.0 2.0 2.0 0.0 2.0 1.0 3.0 0.5 4.0 4.0 53.5 5.35 Marginal
CANUT -
05 Canutillo 2.0 2.0 2.0 0.5 0.0 1.0 4.0 0.5 0.5 4.0 45.0 4.50 Marginal
CANUT -
06 Canutillo 2.0 2.0 2.0 0.5 2.0 0.5 4.0 0.5 3.0 4.0 54.5 5.45 Marginal
LAUNI-
01 La Union 2.0 2.0 2.0 0.5 3.0 1.0 4.0 0.5 0.5 4.0 54.0 5.40 Marginal
LAUNI-
02 La Unioin 2.0 2.0 2.0 0.5 3.0 1.0 3.0 0.5 0.5 4.0 51.0 5.10 Marginal
SECTION 2 -3
Table 2-0, continued: Canutillo Levee Segment Condition Assessment by USACE1
Segment ID Quad
Perfor-mance
Constr History
Visual Insp
Mat’l Type
Topo Irreg
Slope Stab
Man Inrt Geology
Borrow Areas Anom SCORE
Avg Score
Condition Assessment
LAMES-
01 La Mesa 2.0 2.0 2.0 0.5 3.0 1.0 3.0 0.5 4.0 4.0 58.0 5.80 Marginal
LAMES-
02 La Mesa 2.0 2.0 2.0 0.0 2.0 1.0 3.0 0.0 4.0 4.0 55.0 5.50 Marginal
LAMES-
03 La Mesa 2.0 2.0 2.0 0.0 0.0 0.0 3.0 0.0 4.0 4.0 46.0 4.60 Marginal
LAMES-
04 La Mesa 2.0 2.0 2.0 0.5 0.0 0.0 2.0 0.5 4.0 4.0 43.0 4.30 Marginal
LAMES-
05 La Mesa 2.0 2.0 2.0 0.5 1.0 1.0 3.0 0.5 4.0 4.0 52.0 5.20 Marginal
LAMES-
06 La Mesa 2.0 2.0 2.0 0.5 3.0 1.0 4.0 0.5 3.0 4.0 59.0 5.90 Marginal
SECTION 2 -4
The USACE ERDC study also included some limited soil sampling in specific areas using a Site Characterization and Analysis Penetrometer System (SCAPS). Six SCAPS probe locations were within the Canutillo Levee Segment (ST02-01, ST02-02, ST05-01, LM06-01, LM06-02, and LM03-01.) The SCAPS probe findings are discussed on pages 6-37 and 6-39 of the report, and an enlarged image of the ‘EM signature’ of this section of the levee is presented on pages 6-38 and 6-
40. The specific frequencies used in developing this ‘EM signature’ are unclear, but are presumed to be a combination of 25 kHz and 115 kHz survey measurements.
Under the USACE ERDC study, remote sensing of the alignment primarily consisted of an airborne electromagnetic survey using sampling frequencies of 400 Hertz (Hz), 1.5 kilohertz (kHz), 6.2 kHz, 25 kHz and 115 kHz. (Please note that the report text and plates do not agree on the highest frequency employed in this study. R-K has referred to the frequency shown on the plates.) The following statements are found on page 4-12 of the USACE ERDC study:
• Airborne electro-magnetic results for the entire condition assessment study area are perhaps best discussed with reference to the 102 (sic) and 25 kHz frequency data.
Effective depth of investigation at these frequencies is within the body of the levee and immediately below the base of the levees roughly 15 to 20 feet in depth.
• The levees and their shallow foundations on both sides of the Rio Grande from
Garfield, NM to near Fabens, TX (about 30 miles southeast (SE) of El Paso) consist almost entirely of dry, fine-grained sands and silts (with predominantly blue and dark blue airborne EM signatures). These reaches comprise all of the Canalization and a portion of the Rectification levees.
R-K did find some locations with significant thicknesses of clay (e.g. C-1, C-6, C-21, C-110, C- 113, C-173 and C-218.) However, the erratic and discontinuous nature of the encountered clays appears to be consistent with the findings of the EM survey. R-K confirmed the presence of deep gravels at discontinuous locations (C-2, C-67, C-69, C-70 and C-214) like those encountered at SCAPS probe SA01-01. R-K concurs with the ERDC report conclusion that the subsurface soils consist largely of fine-grained sands and silts.
2.3 Risk
The geotechnical engineering design recommendations contained in this report are intended to provide the USIBWC with final design information. R-K has attempted to provide guidance regarding the impact of various design choices on calculated factors of safety with respect to calculated slope stability. The design factors of safety used for this study were taken from USACE EM 1110-2-1913 dated April 30, 2000. The selection of a given design factor of safety implicitly includes a decision regarding the level of acceptable risk for a project. The geotechnical study for this Technical Memorandum did not include an independent evaluation of risk with respect to levee performance, and adopted the published USACE design factors of safety as the current performance standards for these types of structures. Levees are only designed to provide protection to a certain flood level; R-K did not determine the chosen design flood level, and the selection of this parameter is outside R-K’s area of expertise. R-K understands that the USIBWC
SECTION 2 -5
used the computer program FLO-2D to evaluate the water surface profile for the 100-year design flood in accordance with the current FEMA Levee Certification criteria. Furthermore, for the purposes of this Technical Memorandum, it has been assumed that the maximum time that the levee would be subjected to the design flood level is 48 hours or less.
It is important to note that the levee systems are being designed to perform a required function (retain flood waters) under stated conditions (during a 100-year flood event) for a specified period of time (assumed to be 48 hours or less.) The design may not be adequate for a different storm event or longer performance period, and unexpected damage to the levees may result in the need for repairs to the levee and/or levee improvements over time. The enclosed design recommendations inherently assume that the levee will be properly maintained and regularly inspected by trained and qualified personnel. The design recommendations also assume that any identified repairs will be made promptly, and the adequacy of the levee system will be regularly assessed, fully taking into account changes in weather, land use and evolving design and performance standards, with changes made as appropriate.
The geotechnical properties of the soils encountered in this study involve significant variability.
This variability includes some spatial variability; however, the spatial variability appears to occur over relatively short distances. R-K did not observe geological sections along the Canutillo Levee Segment alignment distinct enough to justify subdividing the alignment into subsections for analysis. The basis for this statement is substantiated by findings presented in USACE ERDC /GSL TR-03-04, Report 2, June 2004, as discussed in the Section 2.2 herein. As such, R-K treated the entire alignment as a single unit. It is important to note that levees differ from other types of structures, such as drilled piers or driven piles, in that the performance of the levee involves local, not average, soil conditions.2 The selection of design parameters for this project was based on a review of the available geotechnical data, R-K’s knowledge of the project area, design calculations using idealized geometries and the assumption that the soils are relatively uniform with depth and position on the basis of conditions encountered in R-K’s borings. The results of R-K’s analyses were then reviewed with respect to important trends and general design concepts, keeping these conditions and limitations in mind. R-K’s recommendations are based on a conservative approach to design as is warranted for all levee structures. R-K believes that the combination of observed conditions and probable failure modes justifies this approach.
2.4 Limitations
The geotechnical engineering information within this Technical Memorandum has been prepared in accordance with accepted Geotechnical Engineering practices in the region of southeast New Mexico for the use of the USIBWC, and its representatives for design purposes. This Technical Memorandum may not contain sufficient information for purposes of other parties or other uses.
The recommendations submitted in this Technical Memorandum are based on the data obtained from 253 borings drilled along the alignment of the Canutillo Levee Segment of the Rio Grande Canalization Project; R-K’s understanding of the project information provided by the USIBWC, and the assumptions with regard to water elevations and durations that are discussed in greater detail herein. If the project information described in this report is incorrect, is altered, or if new
SECTION 2 -6
information is available, R-K should be retained to review and modify recommendations contained herein.
The geotechnical engineering information within this Technical Memorandum may not reflect the actual variations of the subsurface conditions across the site. This is particularly true with regard to existing groundwater levels that are likely to be highly variable based on precipitation events and the percent of sands versus fine grained materials. The nature and extent of variations along the levee may not become evident until construction commences. The construction process itself may also alter subsurface conditions. If variations appear evident at the time of construction, it may be necessary for R-K to reevaluate these recommendations after performing on-site observations and tests to establish the engineering impact of the variations.
The scope of this geotechnical exploration / evaluation of the Canutillo Levee Segment does not include an environmental assessment of the air, soil, rock, or water conditions either on or adjacent to the site. No environmental opinions are presented in this Technical Memorandum.
If final added heights along the levee are significantly different from those provided by the USIBWC (more than plus or minus 12-inches), R-K should be informed about these changes. If needed and/or if desired, R-K will reexamine these analyses and make supplemental recommendations.
2.5 Field Exploration
Representatives of R-K made visual observations of the existing levee conditions in conjunction with marking the boring locations in the field. General observations were made of the existing levee configuration including side slopes and vegetative cover.
Subsurface conditions along the Canutillo Levee Segment of the Rio Grande Canalization Project were evaluated by 253 borings. The borings were spaced at approximately every 1,000 feet along the Canutillo Levee Segment alignment, and were drilled to a minimum depth of about 20 to 150 feet. Given the conditions encountered in the project borings and the design recommendations contained in this Technical Memorandum, R-K believes that the number and depth of borings is sufficient for the intended purpose.
The borings were drilled at the locations shown on the Boring Location Map in Exhibit I. The borings are designated C-1 through C-259 and the drilling logs are presented as Figures 2 through 254, of Appendix A-2. The locations shown on the Boring Location Map in Exhibit I and described on the boring logs were provided by S&B. The boring locations were estimated from the boring location maps provided by S&B on July 1, 2008; final locations (after drilling) were field surveyed by the USIBWC, and the results (boring coordinates and elevations), in tabular form, are included in Appendix A-1.
The borings were drilled to depths of about 20 to 150 feet below the existing top of levee using truck-mounted drilling rigs. The borings were advanced using a modified hollow-stem auger
SECTION 2 -7
procedure. Upon completion of drilling, cement-grout was used to backfill holes. During drilling operations, samples were collected as shown in Table 2-1 below.
Table 2-1: Canutillo Levee Segment, Samples Collected
The Shelby tube samples and the SPT’s were obtained in general accordance with accepted standard practices. Grab samples were obtained from auger cuttings along 5 to 10 increments.
Selected portions of the samples were sealed in containers to reduce moisture loss, labeled, packaged, and transported to our laboratory for subsequent testing and classification.
2.6 Laboratory Testing
In the laboratory, each sample was evaluated and visually classified by a member of R-K’s Geotechnical Engineering staff in general accordance with the Unified Soil Classification System (USCS). The geotechnical engineering properties of the strata were evaluated by the laboratory tests tabulated in Table 2-2 on the next page.
With the exception of the laboratory hydraulic conductivity tests and direct shear tests, the results of the field and laboratory tests are presented in graphical or numerical form on the boring logs illustrated on Figures 2 through 254 of Appendix A-2. A key to the classification of terms and symbols used on the logs is presented on Figure 255 of Appendix A-3. The results of the laboratory and field testing are also tabulated on Figure 256 of Appendix A-4 for ease of reference.
SPT results are noted as “blows per foot” on the boring logs and on Figure 255 of Appendix A-3, where “blows per foot” refers to the number of blows required for a falling 140-pound hammer to penetrate 12 inches into the subsurface materials. Where hard and/or very dense materials were encountered, the tests were terminated at 50 blows even if one foot of penetration had not been achieved.
Samples will be retained in the R-K laboratory for 30 days after submittal of the Final Technical Memorandum.
2.6.1 Strength Tests. Multi-stage direct shear tests were performed on 18 selected samples.
These samples were subjected to various normal loads and sheared at a rate of 0.007 inches per minute. Samples tested are composite in nature and were obtained as grab samples from auger cuttings along the depth interval shown. The samples were reconstituted in the lab to simulate in-situ densities in the field. The results of the multi-stage direct shear tests presented graphically and numerically in Appendix B-4, are also summarized in Table 2-3 on the next page.
Type of Sample Number Collected
Canutillo Levee Segment Borings:
Split-Spoon (with SPT) 1964
Shelby Tubes 14
Grab Samples 17
SECTION 2 -8
Type of Test Number Conducted
Natural Moisture Content 1798
Atterberg Limits 1346
Sieve Analysis 785
Percent Passing No. 200 Sieve 521
Hydrometer 12
Unconfined Compressive Strength 5
Dry Unit Weight 14
Multi-Stage Direct Shear 18
Hydraulic Conductivity (Permeability) 49
Table 2-2: Canutillo Levee Segment, Laboratory Tests
Peak Conditions Residual Conditions
Boring
No.
Depth
(ft)
Length
(ft)
Sample Type Friction
Angle, φ deg
Apparent Cohesion tsf
Friction Angle, φ deg
Apparent Cohesion tsf
Visual
Classification
C-15 5 10 Grab 35.8 0.170 35.4 0.103 SM C-30 10 5 Grab 32.9 0.106 33.8 0.021 ML C-40 15 5 Grab 38.6 0.045 38.3 0 ML C-50 10 5 Grab 33.9 0.054 32.5 0.052 SM C-80 7.5 5 Grab 35.3 0.077 35.5 0.026 SM C-90 0 5 Grab 37.6 0.020 37.2 0.028 ML
C-100 5 2 Grab 35.0 0.136 35.0 0.113 SP C-105 10 5 Grab 36.6 0 35.5 0 SP C-120 7.5 5 Grab 36.7 0.070 33.2 0.046 CL C-130 5 10 Grab 36.2 0.048 34.4 0.045 SP-SM C-140 5 10 Grab 31.6 0.194 31.6 0.125 SM C-150 0 5 Grab 35.5 0.107 34.9 0.083 SM C-160 10 5 Grab 35.1 0.066 33.1 0.060 SP-SM C-170 0 5 Grab 34.6 0.055 34.2 0.050 ML C-180 10 5 Grab 34.2 0.184 34.2 0.156 SM C-200 0 5 Grab 34.8 0.024 34.7 0.024 SP C-220 15 5 Grab 39.1 0.048 38.1 0 CL C-249 7.5 2.5 Grab 30.8 0.217 29.0 0.210 CL
Table 2-3: Canutillo Levee Segment, Direct Shear Test Results
SECTION 2 -9
2.6.2 Hydraulic Conductivity (Permeability) Tests. Hydraulic conductivity (permeability) tests were performed on remolded, composite samples obtained from 49 selected samples along the Canutillo Levee Segment. These samples were remolded to simulate in-situ conditions. The remolded specimens were tested for vertical hydraulic conductivity to assess the seepage velocities of the subsurface soils. The results of the hydraulic conductivity (permeability) tests are presented numerically in Appendix B-3, and are also summarized below.
Based on the USACE EM 1110-2-1901 Seepage Analysis and Control for Dams, indirect methods for determining hydraulic conductivity may also be used. For uniform, loose clean sands classified as SP (poorly graded sand), the Hazen equation (Taylor, 1948) is suggested for use. Figure 2-1 below graphically presents the results of hydraulic conductivity testing as well as results calculated using the Hazen equation.
0 50 100 150 200 250 300 Samples Tested
0.0001
0.001
0.01
0.1
H yd ra ul ic C on du ct iv ity , c m /s ec
K values calculated using Hazen formula K values from laboratory testing on reconstituted soil samples
Figure 2-1: Canutillo Levee Segment, Hydraulic Conductivity Test Results
2.7 General Site Conditions
The following outlines the general site conditions of the Canutillo Levee Segment of the Rio Grande Canalization Project.
2.7.1 Site Description. The existing levee system along the project alignment was observed to have heights ranging from 0 to about 10 feet, crest widths between 7 to 30 feet, and
SECTION 2 -10
side slopes as steep as 2:1 (horizontal to vertical). The top of the levees were relatively level and free of vegetation. The side slopes were sparsely covered with some grass and small bushes. Overhead electrical power lines, a few gas lines and several bridges transverse the project alignment at different points along the Rio Grande. A BNSF rail line runs along the entire length of the Canutillo Levee Segment.
There were numerous pecan tree orchards, farm fields, and various residential structures observed along both sides of the project in the Anthony/Vado area. A pedestrian pathway was also observed within the flood plane in this area of the project.
As the project moves towards El Paso (in the Canutillo/Sunland Park area) the number of commercial businesses and residential homes along the river increases. Once in El Paso, the number of residential homes increases and the alignment crosses an industrial zone along the river valley.
This portion of the project alignment mainly traverses open, flat topography. However, hilly and mountain terrain was observed as the alignment approaches the Sunland Park area near El Paso.
2.7.2 Site Geology. The Canutillo Levee Segment is located within the confines of the Rio
Grande Rift, a continental rift belt comprised of echelon extensional basins that originate in central Colorado and extend through New Mexico, and possibly into northern Chihuahua Mexico and west Texas. The Rio Grande Rift is characterized by deep asymmetrical, sedimentary basins, high heat flow from volcanic activity, and Quaternary-age faulting causing basin subsidence and infilling with sediments.3 The sediments have been informally divided into the upper, middle, and lower Santa Fe units which are underlain by Cretaceous age limestones in the southern New Mexico basins, i.e. Mesilla basin, which includes the Canutillo Levee Segment.
The upper Santa Fe sediments are subdivided into the overlying Camp Rice and underlying Fort Hancock Formations which are found within the Mesilla basin of New Mexico and the Hueco Basin of Texas and extend to depths of up to 10,000 feet. The Fort Hancock Formation generally consists of silt and clay basin floor sediments that inter-finger into ephemeral streams originating in the surrounding highlands.3 The sediments were primarily deposited in closed basin lacustrine playas that were fed from ephemeral streams. Exotic clasts are minimal throughout the Fort Hancock formation implying a non-through flowing Rio Grande existed during deposition of the Fort Hancock Formation.3
The Camp Rice Formation consists of fluvial deposited gray coarse-grained, cross-bedded sand and gravel that has incised unconformably into the Camp Rice Formation.4,5,3 Gravel clasts within the Camp Rice Formation comprise a wide variety of distant and local resistant rock type sources.
The specific project setting is located along the levee of the Rio Grande which was
SECTION 2 -11
channelized in the 1930’s as part of a valley-wide flood control and irrigation project.
The Rio Grande Floodplain deposits represent the most recent incision of the Rio Grande into the Camp Rice formation and were deposited during the late Pleistocene through the Holocene Epochs.4,5 The thickness of the Rio Grande Floodplain deposits are up to 200 feet thick comprised of distant and local source sediments ranging from gravel to silt size. Crevasse splays are the typical deposition pattern encountered on the Rio Grande floodplains and are comprised of thin fans of sand and silt.4,5 These sediments are spread across the floodplain during a break in a natural or artificial levee caused by a flood event. The splay grows uniformly progressively coarser and sandier until channels are cut into the top of the splay. These channels are then filled with coarse sediment that becomes progressively finer-grained upward, opposite the majority of the splay deposition.4,5 These channels are discontinuous, often become commingled, and are difficult to correlate across short distances.
2.7.3 Seismic Coefficients. Based upon a review of Section 1615 Earthquake Loads – Site Ground Motion of the 2006 International Building Code (IBC), the following information has been summarized for seismic considerations associated with this site.
Note that the project covers a substantial geographic range. As such, the values taken from the IBC charts also vary across the project. The following parameters are presented as a range and represent the south-eastern most boring (C-1) to the north-western most boring (C-148); these values presented are for Boring HT-1 and Boring C-1 and C-148, respectively.
• Mapped Maximum Considered Earthquake Ground Motion for a 0.2 sec., Spectral
Response Acceleration (Figure 1613.5(1)): Ss = 0.330 to 0.335g.
• Mapped Maximum Considered Earthquake Ground Motion for a 1 sec., Spectral Response Acceleration (Figure 1613.5(2)): S1 = 0.105 to 0.106g.
2.7.4 Stratigraphy. The subsurface conditions observed in the borings performed for this study were relatively consistent along the entire length of levee. Levee fill soils consisting of locally available soils were observed at the levee crest, extending to the natural ground elevations. These fill soils were observed at depths ranging from about 12 ft to areas without any existing levee structure. Like the other canalization segments, sands were the predominate fill material observed in our borings (about 63% based on layer depths). The remaining portion of the fill materials consisted of about 30% silts and 7% clays.
Beneath the fill soils, predominately naturally deposited sands and gravels (about 81% based on layer depths) were found to depths of about 20 to 150 ft, the maximum depths explored. As with any linear project that cross spatially diverse conditions, a number of cohesive soil layers (about 12% based on depth) and layers with varying silt fractions (about 7% based on depth) were observed at different depths and thicknesses. A detailed exposition of these variances is not addressed in this text. However, a detailed
SECTION 2 -12
description of the soil conditions observed at each boring location has been presented in the Boring Logs, Figures 2 through 254, of Appendix A. The lines designating the interfaces between strata on the boring logs represent approximate boundaries.
Transitions between strata may be gradual.
The predominate soils observed in the borings were classified as poorly graded sands (SP), poorly graded sands with silt (SP-SM), and silty sands (SM). However, areas of well graded gravels (GW), well graded sands with silt (SW-SM), clayey sands (SC), lean clays with sand (CL), fat clays with sand (CH), silts with sand (ML), and sandy silty clays (CL-ML) were also observed. In particular, deep gravels were observed in Borings C-67, C-69, and C-70.
2.8 Impact of Sampling / Testing Procedures on Measured and Design Soil Properties
2.8.1 Permeability. Soils were deposited along the Rio Grande floodplain through a series of natural processes, primarily by transport by water and wind. The soils beneath the levee embankments are primarily sands and were generally deposited by the Rio Grande river system, with some relatively thin, fine layers of sand and silt deposited by wind during dust storms. The soil deposits exhibit spatial variability, with resulting anisotropy inherent in the gradation and permeability of the natural deposits. In general, the horizontal permeability of the soil strata are expected to be at least 2 to 5 times greater than their vertical permeability.
The man-made sand embankments also expected to exhibit some spatial variability, although the variations would not seem to be as great as the variations within the natural soil deposits. However, the process of constructing the levees by compacting soils in relatively thin lifts can also result in significantly greater horizontal permeability compared to vertical permeability. Each lift required a finite amount of time to construct; the interfaces between lifts often dry out and develop a thin layer of loose surficial soils, which exhibit a higher permeability than the soils in the middle of the lift. It is also likely that the sands were compacted dry of their optimum moisture content using non-vibratory smooth drum compaction equipment. Soils compacted dry of optimum moisture content exhibit significantly higher field permeability than the same soils compacted to the same density, but wet of optimum moisture content.
Smooth drums on compaction equipment are not capable of generating the kneading action needed to mechanically destroy the inter-lift discontinuity in the compacted soil lifts. All of these factors permit the development of higher horizontal permeability than might be expected. These factors are exacerbated if the construction contractor also used fairly thick compaction lifts.
The potential impacts of natural soil and compacted soil fill layering on permeability are significant. Under ideal conditions, the field exploration and laboratory testing programs would be aimed at harvesting and testing undisturbed soil samples so that the in-place soil permeability could be measured. Unfortunately, the predominate soil
SECTION 2 -13
types encountered in this study are very difficult to sample and test in an undisturbed condition. As a result, conventional practice is to obtain disturbed soil samples and perform the various laboratory tests on reconstituted, or remolded, samples, and to make adjustments to the measured values when evaluating their probable behavior in the field. The sampling process destroys the structure and orientation of layers of differing characteristics, and distributes the fine-grained silt and clay fraction throughout the bulk sample. The process of harvesting large volumes of soil and remolding samples has the effect of homogenizing the samples, generally resulting in lower tested permeability. The impact on tested permeability can be significant.
Laboratory measured permeability can be several orders of magnitude lower than the actual maximum field permeability.
The laboratory permeability tests were conducted using ordinary tap water as the permeate in accordance with industry practice. This choice can affect the tested permeability where the soils contain significant amounts of soluble salts, or the tap water contains unusually high amounts of total dissolved solids (TDS). R-K does not believe that the tested samples contained significant amounts of TDS, and the tap water used in the tests meets current Environmental Protection Agency’s (EPA) drinking water standards. Given the soil types tested for this study, R-K does not believe that changes in the tested samples’ TDS, if any, had a significant impact on the measured results.
The laboratory permeability tests were performed using hydraulic gradients as high as
30. This test condition is much higher than the typical expected field gradient of less than 0.5. Excessive laboratory hydraulic gradients can cause migration of silt and clay particles within the sample, significantly reducing the measured permeability.
However, R-K does not believe that particle migration significantly affected the test results. Particle migration often occurs when the gradient is applied instantaneously.
The test gradient was gradually applied over several minutes in an effort to avoid this problem.
2.8.2 Inferred Permeability. The laboratory grain size analyses were used in conjunction with the Hazen6 formula to provide an estimate of permeability. The Hazen formula was developed using filter sands with effective sizes between 0.1 and 3 millimeters and uniformity coefficients of less than 5. For this limited range of clean sands, permeability estimates computed using the formula generally was within 20 percent (20%) of the measured values.
The soils tested for this study generally do not meet the effective size or fines fraction requirements of the soils Allen Hazen used to develop his correlation. However, in many cases, the effective sizes of the tested sands are close enough to the sands tested by Hazen that the equation can be used to provide some indication of the variability of permeability of the soils.
This is the start of the file's text. The full file is on GovTribe.
File details come from the government source that posted it. Updated .