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HomeMy WebLinkAbout5208-A; RECYCLED WATER PHASE III PIPELINE EXPANSION SEGMENT 9; GEOTECHNICAL EVALUATION; 2016-06-14GEOTECHNICAL EVALUATION RECYCLED WATER PHASE III PIPELINE SEGMENT 9 PROJECT CARLSBAD, CALIFORNIA PREPARED FOR: Infrastructure Engineering Corporation 14271 Danielson Street Poway, California 92064 PREPARED BY: Ninyo & Moore Geotechnical and Environmental Sciences Consultants 5710 Ruffin Road San Diego, California 92123 June 14, 2016 Project No. 108153001 5208-A Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc i TABLE OF CONTENTS Page 1. INTRODUCTION ....................................................................................................................1 2. SCOPE OF SERVICES ............................................................................................................1 3. PROJECT AND SITE DESCRIPTION ...................................................................................2 4. FIELD EXPLORATION AND LABORATORY TESTING ..................................................2 5. GEOLOGY AND SUBSURFACE CONDITIONS .................................................................3 5.1. Regional and Geologic Setting .....................................................................................3 5.2. Site Geology .................................................................................................................4 5.2.1. Fill .......................................................................................................................4 5.2.2. Old Paralic Deposits ............................................................................................4 5.3. Groundwater .................................................................................................................4 6. GEOLOGIC HAZARDS ..........................................................................................................5 6.1. Faulting and Seismicity ................................................................................................5 6.1.1. Ground Surface Rupture .....................................................................................5 6.1.2. Strong Ground Motions ......................................................................................5 6.1.3. Liquefaction and Seismically Induced Settlement ..............................................6 6.2. Landsliding ...................................................................................................................6 7. CONCLUSIONS ......................................................................................................................7 8. RECOMMENDATIONS ..........................................................................................................8 8.1. Earthwork .....................................................................................................................8 8.1.1. Site Preparation ...................................................................................................8 8.1.2. Excavation Characteristics ..................................................................................8 8.1.3. Temporary Excavations and Shoring ..................................................................9 8.1.4. Excavation Bottom Stability .............................................................................10 8.1.5. Pipe Bedding and Pipe Zone Backfill ...............................................................10 8.1.6. Modulus of Soil Reaction (E') ...........................................................................10 8.1.7. Trench Zone Backfill Materials ........................................................................11 8.1.8. Fill Placement and Compaction ........................................................................11 8.2. Lateral Pressures for Thrust Blocks and Jacking ........................................................12 8.3. Pavement Reconstruction ...........................................................................................12 8.4. Corrosivity ..................................................................................................................12 8.5. Concrete Placement ....................................................................................................13 8.6. Pre-Construction Conference ......................................................................................13 8.7. Plan Review and Construction Observation ...............................................................13 9. LIMITATIONS .......................................................................................................................14 10. REFERENCES .......................................................................................................................16 Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc ii Figures Figure 1 – Site Location Figure 2 – Boring Locations Figure 3 – Fault Locations Figure 4 – Geology Figure 5 – Lateral Earth Pressures for Braced Excavation Figure 6 – Thrust Block Lateral Earth Pressure Diagram Appendices Appendix A – Boring Logs Appendix B – Laboratory Testing Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 1 1. INTRODUCTION In accordance with your request and our proposal dated January 4, 2016, we have performed a geotechnical evaluation for the proposed Recycled Water Phase III, Pipeline Segment 9 Project located in Carlsbad, California (Figure 1). This report presents our findings and conclusions regarding the geotechnical conditions along the subject alignments and our recommendations for the design and construction of this project. 2. SCOPE OF SERVICES Ninyo & Moore’s scope of services for this project included review of pertinent background da- ta, performance of a geologic reconnaissance, subsurface exploration, and engineering analysis with regard to the proposed project. Specifically, we performed the following tasks:  Reviewing background information including available topographic maps, geologic data, fault maps, aerial photographs, and a provided alignment figure.  Coordinating and mobilizing for a geotechnical reconnaissance to observe the existing site conditions and to mark-out the boring locations for utility clearance by Underground Service Alert (USA).  Obtaining traffic control plans from a traffic control subcontractor and right of way permits from the City of Carlsbad.  Performing a subsurface exploration program consisting of excavating, logging, and sampling of four exploratory borings.  Performing geotechnical laboratory testing on representative soil samples to evaluate ge- otechnical characteristics and design parameters.  Performing geotechnical analysis of the data obtained from our site reconnaissance, subsur- face exploration, and laboratory testing.  Preparing this report presenting our findings, conclusions, and recommendations regarding the geotechnical design and construction of the project. Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 2 3. PROJECT AND SITE DESCRIPTION We understand that the project will consist of expanding the existing recycled water piping sys- tem for the City of Carlsbad. This project area is referred to as Pipeline Segment 9. Pipeline Segment 9 will include the installation of 1,420 lineal feet of 8-inch diameter polyvinyl chlo- ride (PVC) piping along Ponto Drive, 1,460 lineal of 6-inch diameter PVC piping along Navigator Circle, and 1,750 lineal feet of 8-inch diameter PVC piping along Avenida Encinas. The invert depths of the piping are anticipated to be approximately 4 1/2 feet below finished ground surface. The new segments will connect to the existing recycled water line at two inter- connection vaults, which are to be located at the intersection of Poinsettia Lane and Avenida Encinas and at the intersection of Ponto Drive and Avenida Encinas. Surface elevations along Pipeline Segment 9 range from a low of approximately 40 feet above mean sea level (MSL) near the north end of Ponto Drive to a high of approximately 105 feet above MSL at the east portion of Navigator Circle. 4. FIELD EXPLORATION AND LABORATORY TESTING Our subsurface exploration was conducted on May 17, 2016 and consisted of drilling, logging, and sampling of four small-diameter exploratory borings (B-1 through B-4). The borings were drilled to depths up to approximately 16 ½ feet using a truck-mounted drill rig equipped with 8-inch diameter, hollow-stem augers. During the drilling operations, the borings were logged and sampled by Ninyo & Moore personnel. Representative bulk and in-place soil samples were obtained from within the borings. The samples were then transported to our in-house geotechnical laboratory for testing. The approximate locations of the exploratory borings are shown on Figure 2. As depicted on Figure 2, boring B-1 was performed within the area for the pipeline expansion along Avenida Encinas, borings B-2 and B-3 were performed within the area for the pipeline expansion along Ponto Drive, and boring B-4 was performed within the area for the pipeline expansion along Navigator Circle. Logs of the borings are included in Appendix A. Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 3 The geotechnical laboratory testing that was performed on representative soil samples included an evaluation of in-situ dry density and moisture content, gradation (sieve) analysis, shear strength, and soil corrosivity. The results of the in-situ dry density and moisture content tests are presented on the boring logs in Appendix A. The results of the other laboratory tests are present- ed in Appendix B. 5. GEOLOGY AND SUBSURFACE CONDITIONS Our findings regarding regional and site geology along with groundwater conditions at the pro- ject alignments are provided in the following sections. 5.1. Regional and Geologic Setting The project area is situated in the coastal foothill section of the Peninsular Ranges Geo- morphic Province. This geomorphic province encompasses an area that extends approximately 900 miles from the Transverse Ranges and the Los Angeles Basin south to the southern tip of Baja California (Harden, 2004; Norris and Webb, 1990). The province varies in width from approximately 30 to 100 miles. In general, the province consists of rug- ged mountains underlain by Jurassic metavolcanic and metasedimentary rocks, and Cretaceous igneous rocks of the Southern California Batholith. The portion of the province in San Diego County that includes the project area consists generally of Quaternary and Ter- tiary age sedimentary rock. The Peninsular Ranges Province is traversed by a group of sub-parallel faults and fault zones trending roughly northwest. Several of these faults, which are shown on Figure 3, are considered active faults. The Elsinore, San Jacinto, and San Andreas faults are active fault systems located northeast of the project area and the Rose Canyon, Coronado Bank, San Di- ego Trough, and San Clemente faults are active faults located west of the project area. The Rose Canyon Fault Zone, the nearest active fault system, has been mapped less than 4 miles west of the project alignments. Major tectonic activity associated with these faults within this regional tectonic framework consists primarily of right-lateral, strike-slip movement. Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 4 5.2. Site Geology Geologic units encountered during our reconnaissance and subsurface exploration in- cluded fill and old paralic deposits (Kennedy and Tan, 2007). Generalized descriptions of the earth units encountered are provided in the subsequent sections. Additional de- scriptions of the subsurface units are provided on the boring logs in Appendix A. For further reference, a geologic map of the region is presented on Figure 4. 5.2.1. Fill Fill was encountered in each of our exploratory borings beneath the pavement sections and extending to depths up to approximately 8 feet. As encountered, the fill generally consisted of various shades of brown and gray, moist, medium dense, silty sand. Gravel and brick fragments were observed within the encountered fill materials. 5.2.2. Old Paralic Deposits Quaternary-age old paralic deposits were encountered in our exploratory borings underlying the fill materials and extending to the total depth explored of approximately 16 ½ feet. As encountered, the old paralic deposits generally consisted of various shades of brown, moist, medium dense to very dense, silty sand. 5.3. Groundwater Groundwater was not encountered during our subsurface exploration. Our review of back- ground documents indicates that groundwater is present at depths greater than 20 feet. However, soils above their optimum moisture were encountered in our boring B-2 just be- low the pavement section. Additionally, existing utility trench lines may act as conduits for perched water conditions. Due to the site topography, nearby areas of landscaping, and the potential presence for existing utility trench lines, zones of seepage and/or perched water should be anticipated. Fluctuations in the groundwater level and perched water conditions may occur due to variations in ground surface topography, subsurface geologic conditions and structure, rainfall, irrigation, tidal fluctuations, and other factors. Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 5 6. GEOLOGIC HAZARDS In general, hazards associated with seismic activity include ground surface rupture, strong ground motion, liquefaction, and landslides. These considerations are discussed in the following sections. 6.1. Faulting and Seismicity The project area is considered to be seismically active. Based on our review of the refer- enced geologic maps and stereoscopic aerial photographs, as well as our geologic field reconnaissance, the subject alignments are not underlain by known active or potentially ac- tive faults (i.e., faults that exhibit evidence of ground displacement in the last 11,000 years and 2,000,000 years, respectively). Major known active faults in the region consist generally of en-echelon, northwest-striking, right-lateral, strike-slip faults. These include the Rose Canyon, Coronado Bank, San Diego Trough, and San Clemente faults, located to the west of the site, and the Elsinore, San Jacinto and San Andreas faults, located to the east of the site. The locations of these faults are shown on Figure 3. The closest known active fault is the Rose Canyon fault, which can generate an earthquake maximum moment magnitude Mmax of up to 7.2 as published for the CGS by Cao et al. (2003). It is located less than 4 miles west of the project segments. 6.1.1. Ground Surface Rupture Based on our review of the referenced literature and our site reconnaissance, no active faults are known to cross the project site or pipeline alignments. Therefore, the potential for ground rupture due to faulting at the site is unlikely. However, lurching or cracking of the ground surface as a result of nearby seismic events is possible. 6.1.2. Strong Ground Motions The 2013 California Building Code (CBC) specifies that the Risk-Targeted, Maximum Considered Earthquake (MCER) ground motion response accelerations be used to eval- uate seismic loads for design of buildings and other structures. The MCER ground motion response accelerations are based on the spectral response accelerations for Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 6 5 percent damping in the direction of maximum horizontal response and incorporate a target risk for structural collapse equivalent to 1 percent in 50 years with deterministic limits for near-source effects. The horizontal peak ground acceleration (PGA) that cor- responds to the MCER for the segments was calculated as 0.47g using the United States Geological Survey (USGS, 2016) seismic design tool (web-based). The 2013 CBC specifies that the potential for liquefaction and soil strength loss be evaluated, where applicable, for the Maximum Considered Earthquake Geometric Mean (MCEG) peak ground acceleration with adjustment for site class effects in accordance with the American Society of Civil Engineers (ASCE) 7-10 Standard. The MCEG peak ground acceleration is based on the geometric mean peak ground acceleration with a 2 percent probability of exceedance in 50 years. The MCEG peak ground acceleration with adjustment for site class effects (PGAM) was calculated as 0.48g using the USGS (USGS, 2016) seismic design tool that yielded a mapped MCEG peak ground accelera- tion of 0.47g for the site and a site coefficient (FPGA) of 1.032 for Site Class D. 6.1.3. Liquefaction and Seismically Induced Settlement Liquefaction of cohesionless soils can be caused by strong vibratory motion due to earthquakes. Research and historical data indicate that loose granular soils and non- plastic silts that are saturated by a relatively shallow groundwater table are susceptible to liquefaction. Based on the relatively dense nature of the old paralic deposits underly- ing the pipeline alignments, liquefaction and the resulting seismically induced settlements are not design considerations. 6.2. Landsliding No landslides or indications of deep-seated landslides were noted underlying the project site dur- ing our field exploration or our review of available geologic literature and topographic maps. Our review of Tan (1995) indicates that the alignment is situated in Landslide Susceptibility Ar- ea 2, which represents areas that are marginally susceptible to landsliding. Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 7 7. CONCLUSIONS Based on our review of the referenced background data and the results of our subsurface explora- tion, it is our opinion that construction of the proposed project is feasible from a geotechnical standpoint provided that the recommendations of this report are incorporated into the preliminary design of the project. Geotechnical considerations include the following:  Based on the results of our background review and subsurface exploration, the geologic units that underlie the project segments include fill and old paralic deposits.  The on-site fill and old paralic deposits should be generally excavatable with conventional heavy-duty earth moving construction equipment in generally good condition.  Materials derived from on-site excavations are generally considered suitable for reuse as back- fill, provided they meet the recommendations for backfill materials presented in the following sections.  Due to the granular nature of the fill and old paralic deposits in the vicinity of our exploratory borings, the contractor should anticipate encountering caving and/or sloughing conditions when excavating these materials.  Although groundwater was not encountered, soils above optimum moisture content were en- countered in boring B-2. Additionally, perched water conditions may be present within the project alignment areas. The contractor should be prepared to address issues associated with seepage and perched water conditions such as excavation stability, dewatering, and the pres- ence of soils above optimum moisture content proposed for reuse as backfill material.  Soils above their optimum moisture content were encountered during our subsurface explo- ration within boring B-2. Therefore, the contractor should anticipate additional processing of these materials (including aeration) prior to reuse as backfill.  Based on the soil corrosivity testing presented in Appendix B, test results indicate the soils along the project alignments are not considered corrosive based on ACI 318 and Caltrans corrosion criteria (2012).  No active faults are reported underlying or adjacent to the alignments. The active Rose Can- yon fault has been mapped less than 4 miles west of the segments. Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 8 8. RECOMMENDATIONS The following sections include our geotechnical recommendations for the design of the proposed project. These recommendations are based on our evaluation of the site geotechnical conditions and our understanding of the planned construction. 8.1. Earthwork In general, earthwork should be performed in accordance with the recommendations pre- sented in this report. Ninyo & Moore should be contacted for questions regarding the recommendations or guidelines presented herein. 8.1.1. Site Preparation Prior to performing site excavations, the site should be cleared of vegetation, surface obstructions, rubble and debris, abandoned utilities and foundations, and other deleteri- ous materials. Existing utilities within the project limits, if any, should be re-routed or protected from damage by construction activities. Obstructions that extend below finish grade, if any, should be removed and the resulting holes filled with compacted soils. Materials generated from the clearing operations should be removed from the project site and disposed of at a legal dumpsite. 8.1.2. Excavation Characteristics Our evaluation of the excavation characteristics of the on-site materials is based on the results of our exploratory borings, our site observations, and our experience with similar materials. In our opinion, the existing fill and old paralic deposits are generally expected to be rippable with heavy-duty trenching equipment to the anticipated construction depths. Due to the granular nature of the fill and old paralic deposits in the vicinity of our exploratory borings, the contractor should anticipate encountering caving and/or sloughing conditions when excavating these materials. Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 9 8.1.3. Temporary Excavations and Shoring For temporary excavations, we recommend that the following Occupational Safety and Health Administration (OSHA) soil classifications be used: Fill and Old Paralic Deposits Type C Upon making the excavations, the soil classifications and excavation performance should be evaluated in the field by the geotechnical consultant in accordance with the OSHA regulations. Temporary excavations should be constructed in accordance with OSHA recommendations. For trenches or other excavations, OSHA requirements re- garding personnel safety should be met using appropriate shoring (including trench boxes) or by laying back the slopes to no steeper than 1.5:1 (horizontal to vertical) in fill and old paralic deposits. Temporary excavations that encounter seepage may be shored or stabilized by placing sandbags or gravel along the base of the seepage zone. Excavations encountering seepage should be evaluated on a case-by-case basis. On-site safety of personnel is the responsibility of the contractor. In areas with limited space for construction where temporary excavations may not be laid back at the recommended slope inclination, a shoring system with bracing may be incor- porated to stabilize the excavation sidewalls during construction. The shoring system should be designed using the magnitude and distribution of lateral earth pressures pre- sented on Figure 5. The recommended design earth pressures are based on the assumptions that (a) the shoring system is constructed without raising the ground surface elevation behind the shoring, (b) that there are no surcharge loads, such as soil stockpiles, construction materials, construction equipment, or vehicular traffic, and (c) that no loads act above a 1:1 plane extending up and back from the base of the shoring system. For shoring subjected to the above-mentioned surcharge loads, the contractor should include the effect of these loads on lateral earth pressures acting on the shoring wall. Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 10 8.1.4. Excavation Bottom Stability In general, we anticipate that the bottom of the excavations will be stable and should provide suitable support to the proposed pipeline. Excavations which are close to or ex- tend below the water table (if encountered) may be unstable. In general, unstable bottom conditions may be mitigated by overexcavating the excavation bottom to suita- ble depths and replacing with a 6 to 12-inch layer of compacted ¾ to 1½-inch crushed gravel, that is encased in Mirafi® 600X woven geotextile, or an approved equivalent. Recommendations for stabilizing excavation bottoms should be based on evaluation in the field by the geotechnical consultant at the time of construction. 8.1.5. Pipe Bedding and Pipe Zone Backfill We recommend that pipes be supported on 6 inches or more of granular bedding materi- al. Pipe bedding and pipe zone backfill typically consists of graded aggregate with a coefficient of uniformity of three or more. Pipe bedding and pipe zone backfill should be sand that has a Sand Equivalent (SE) of 30 or more with no material larger than 1/2-inch (City of Carlsbad, 2016a). These materials should be placed below, around the sides, and on top of the pipe. In addition, the pipe zone backfill should extend 1 foot or more above the top of the pipe (City of Carlsbad, 2016b). It has been our experience that the voids within a crushed rock material are sufficiently large to allow fines to migrate into the voids, thereby creating the potential for sinkholes and depressions to develop at the ground surface. If open-graded gravel is utilized as pipe zone backfill, this material should be separated from the adjacent trench sidewalls and overlying trench backfill with a geosynthetic filter fabric. 8.1.6. Modulus of Soil Reaction (E') The modulus of soil reaction (E') is used to characterize the stiffness of soil backfill placed at the sides of buried flexible pipes for the purpose of evaluating deflection caused by the weight of the backfill over the pipe (Hartley and Duncan, 1987). A soil reaction modulus of 1,200 pounds per square inch (psi) may be used for an excavation depth of up to about Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 11 5 feet when backfilled with granular soil compacted to a relative compaction of 90 percent as evaluated by the ASTM International (ASTM) D 1557. A soil reaction modulus of 1,800 psi may be used for trenches deeper than 5 feet. 8.1.7. Trench Zone Backfill Materials In general, on-site soils with an organic content of less than approximately 3 percent by volume (or 1 percent by weight) that meet the following gradations are considered suit- able for reuse as trench zone backfill. For the purpose of this report, the trench zone is considered to extend from 1 foot above the top of the pipe to the top of the trench. The backfill material should not generally contain rocks or lumps larger than approximately 3 inches, and particles not more than approximately 30 percent larger than ¾ inch. Larger chunks, if generated during excavation, may be broken into acceptably sized pieces or disposed of offsite. Imported fill material, if needed for the project, should generally be granular soils. Materials for use as backfill should be evaluated by Ninyo & Moore’s representative prior to filling or importing. 8.1.8. Fill Placement and Compaction Fill and trench backfill should be compacted by mechanical methods in horizontal lifts to a relative compaction of 90 percent as evaluated by the latest edition of ASTM D 1557. The upper 12 inches of street subgrade and aggregate base materials beneath pavement areas should be compacted to a relative compaction of 95 percent. Fill and trench backfill soils should be placed at or above the laboratory optimum mois- ture content as evaluated by the latest edition of ASTM D 1557. The optimum lift thickness of fill will depend on the type of compaction equipment used, but generally should not exceed 8 inches in loose thickness. Successive lifts should be treated in a like manner until the desired finished grades are achieved. Special care should be taken to avoid pipe damage when compacting trench backfill above the pipe. Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 12 8.2. Lateral Pressures for Thrust Blocks and Jacking Thrust restraint for buried pipelines and lateral pressures for jacking may be achieved by trans- ferring the thrust force to the soil outside the pipe through a thrust block. Thrust blocks may be designed using the lateral passive earth pressures presented on Figure 6. Thrust blocks should be backfilled with granular backfill material, compacted as outlined in this report. 8.3. Pavement Reconstruction Trench excavations in existing pavement areas may involve replacement of pavements as part of the work. In general, trench pavement repair should include asphalt concrete (AC) that is 1 inch thicker than the existing AC pavement section, and be 4 inches or more in thickness. Also the AC and aggregate base materials should conform to the material thick- nesses and compaction requirements of the adjacent pavement section. Subgrade and aggregate base materials should be compacted to 95 percent relative compaction as evaluat- ed by ASTM D 1557. AC should be compacted to 95 percent relative compaction as evaluated by ASTM D1561 (Hveem density). Actual pavement reconstruction should con- form to the requirements of the city/agency of jurisdiction. 8.4. Corrosivity Laboratory testing was performed on representative samples of near-surface soils to evaluate soil pH, electrical resistivity, water-soluble chloride content, and water-soluble sulfate con- tent. The soil pH and electrical resistivity tests were performed in general accordance with California Test (CT) 643. Chloride content tests were performed in general accordance with CT 422. Sulfate testing was performed in general accordance with CT 417. The laboratory test results are presented in Appendix B. The pH values of the tested samples ranged from 6.9 to 7.1. The electrical resistivities of the tested samples ranged from approximately 3,300 to 18,000 ohm-centimeters. The chloride contents of the tested samples ranged from approximately 65 to 140 ppm. The sulfate con- tents of the tested samples ranged from approximately 0.002 to 0.009 percent by weight (i.e., 20 to 90 ppm). Based on the laboratory test results, as compared to ACI 318 and Cal- Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 13 trans (2012) corrosion criteria, the soils along the project alignments would not be classified as corrosive, which is defined as having earth materials with an electrical resistivity of less than 1,000 ohm-centimeters, more than 500 ppm chlorides, more than 0.10 percent sulfates (i.e., 1,000 ppm), and/or a pH of 5.5 or less. 8.5. Concrete Placement Concrete in contact with soil or water that contains high concentrations of soluble sulfates can be subject to chemical deterioration. Laboratory testing indicated sulfate contents ranging from approximately 0.002 to 0.009 percent, which is considered to represent a negligible po- tential for sulfate attack (ACI, 318). However, due to the potential for variability of soils, the proximity of the pipeline segments to the Pacific Ocean, and the potential use of recycled wa- ter, we recommend using Type II/V or V cement for concrete structures in contact with soil. 8.6. Pre-Construction Conference We recommend that a pre-construction meeting be held prior to commencement of construc- tion. The owner or his representative, the agency representatives, the civil engineer, Ninyo & Moore, and the contractor should be in attendance to discuss the plans, the project, and the proposed construction schedule. 8.7. Plan Review and Construction Observation The conclusions and recommendations presented in this report are based on analysis of ob- served conditions. If conditions are found to vary from those described in this report, Ninyo & Moore should be notified, and additional recommendations will be provided upon request. Ninyo & Moore should review the project drawings and specifications prior to the commencement of construction. Ninyo & Moore should perform the needed observation and testing services during construction operations. Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 14 The recommendations provided in this report are based on the assumption that Ninyo & Moore will provide additional geotechnical evaluations during design of the project and ge- otechnical observation and testing services during construction. In the event that it is decided not to utilize the services of Ninyo & Moore during construction, we request that the selected consultant provide the client with a letter (with a copy to Ninyo & Moore) indi- cating that they fully understand Ninyo & Moore’s recommendations, and that they are in full agreement with the design parameters and recommendations contained in this report. Construction of proposed improvements should be performed by qualified subcontractors utilizing appropriate techniques and construction materials. 9. LIMITATIONS The field evaluation, laboratory testing, and geotechnical analyses presented in this geotechnical report have been conducted in general accordance with current practice and the standard of care exercised by geotechnical consultants performing similar tasks in the project area. No warranty, expressed or implied, is made regarding the conclusions, recommendations, and opinions pre- sented in this report. There is no evaluation detailed enough to reveal every subsurface condition. Variations may exist and conditions not observed or described in this report may be encountered during construction. Uncertainties relative to subsurface conditions can be reduced through addi- tional subsurface exploration. Additional subsurface evaluation will be performed upon request. Please also note that our evaluation was limited to assessment of the geotechnical aspects of the project, and did not include evaluation of structural issues, environmental concerns, or the pres- ence of hazardous materials. This document is intended to be used only in its entirety. No portion of the document, by itself, is designed to completely represent any aspect of the project described herein. Ninyo & Moore should be contacted if the reader requires additional information or has questions regarding the content, interpretations presented, or completeness of this document. Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 15 This report is intended for design purposes only. It does not provide sufficient data to prepare an accurate bid by contractors. It is suggested that the bidders and their geotechnical consultant per- form an independent evaluation of the subsurface conditions in the project areas. The independent evaluations may include, but not be limited to, review of other geotechnical reports prepared for the adjacent areas, site reconnaissance, and additional exploration and laboratory testing. Our conclusions, recommendations, and opinions are based on an analysis of the observed site conditions. If geotechnical conditions different from those described in this report are encountered, our office should be notified and additional recommendations, if warranted, will be provided upon request. It should be understood that the conditions of a site could change with time as a result of natural processes or the activities of man at the subject site or nearby sites. In addition, changes to the applicable laws, regulations, codes, and standards of practice may occur due to government ac- tion or the broadening of knowledge. The findings of this report may, therefore, be invalidated over time, in part or in whole, by changes over which Ninyo & Moore has no control. This report is intended exclusively for use by the client. Any use or reuse of the findings, conclu- sions, and/or recommendations of this report by parties other than the client is undertaken at said parties’ sole risk. Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 16 10. REFERENCES American Concrete Institute, 2011, ACI 318 Building Code Requirements for Structural Con- crete (ACI 318) and Commentary (ACI 318R). American Society of Civil Engineers (ASCE), 2010, Minimum Design Loads for Buildings and Other Structures, ASCE 7-10. California Building Standards Commission (CBSC), 2013, California Building Code (CBC), Ti- tle 24, Part 2, Volumes 1 and 2: dated June. California Department of Conservation Division of Mines and Geology (CDMG), 1998, Maps of Known Active Fault Near-Source Zones in California and Adjacent Portions of Nevada: dated February. California Department of Transportation (Caltrans), 2012, Corrosion Guidelines, Version 2.0, Division of Engineering Services, Materials Engineering and Testing Services, Corrosion and Structural Concrete Field Investigation Branch: dated November. Cao, T., Bryant, W. A., Rowshandel, B., Branum, D., and Willis, C. J., 2003, The Revised 2002 California Probabilistic Seismic Hazards Maps: California Geological Survey: dated June. City of Carlsbad, 2016a, Engineering Standards, Volume 2, Potable and Recycled Water Standards. City of Carlsbad, 2016b, Engineering Standards, Volume 3, Standard Drawings and Specifications. Geotracker, 2016, http://geotracker.swrcb.ca.gov/: accessed in May. Google, Inc., 2016, www.googleearth.com: accessed in May. Harden, D.R., 2004, California Geology, 2nd Edition: Prentice Hall, Inc. Hartley, J.D., and Duncan, J.M., 1987, E’ and Its Variation with Depth: American Society of Civil Engineers (ASCE), Journal of Transportation Engineering, Vol. 113, No. 5: dated September. Jennings, C.W., 2010, Fault Activity Map of California and Adjacent Areas: California Geologi- cal Survey, California Geologic Data Map Series, Map No. 6, Scale 1:750,000. Kennedy, M.P., and Tan, S.S., 2007, Geologic Map of the Oceanside 30’ x 60’ Quadrangle, Califor- nia, Scale 1:100,000. Ninyo & Moore, In-House Proprietary Data. Ninyo & Moore, 2016, Revised Proposal for Geotechnical Evaluation, OMWD Recycled Water Pipeline, Segment 9, Carlsbad, California, Proposal No P02-00429: dated January 4. Norris, R. M. and Webb, R. W., 1990, Geology of California, Second Edition: John Wiley & Sons, Inc. Public Works Standards, Inc., 2015, “Greenbook,” Standard Specifications for Public Works Con- struction. Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc 17 Tan, S.S., 1995, Landslide Hazards in the Northern Part of the San Diego Metropolitan Area. Treiman, J.A., 1993, The Rose Canyon Fault Zone, Southern California: California Geological Survey, Open File Report 93-02. United States Department of the Interior, Bureau of Reclamation, 1998, Engineering Geology Field Manual. United States Geological Survey, 2015, Encinitas Quadrangle, California, San Diego County, 7.5-Minute Series (Topographic): Scale 1:24,000. United States Geological Survey, 2016, Seismic Design Maps Application, http://earthquake.usgs.gov/designmaps/us/application.php: accessed in May. AERIAL PHOTOGRAPHS Source Date Flight Numbers Scale United States Department of Agriculture 4-11-53 AXN-8M 97 and 98 1:20,000 Navigator CrNOTE: DIRECTIONS, DIMENSIONS AND LOCATIONS ARE APPROXIMATE 1_108153001_SL_93.mxd AOB88 5 15 805805 215215 MAP INDEX San DiegoCounty 0 1,500 3,000750 SCALE IN FEET RECYCLED WATER PHASE III PIPELINE SEGMENT 9 PROJECT CARLSBAD, CALIFORNIA SITE LOCATION FIGURE 1PROJECT NO.DATE 108153001 6/16 SOURCE: USGS, FAO, NPS, EPA, ESRI, DELORME, TANA, OTHER SUPPLIERS LEGEND SITE LOCATION B-3TD=16.5 B-2 TD=15.9 B-1 TD=16.5 5 B-4 TD=16.5 WI N D RO S E CIRCLENAVIGATOR CIRCLECARL SBAD BOUL EVARDA V E NI DA E N C IN A S PO I NS E T T I A L AN E P O N T O D R IV E P O N T O R D NOTE: DIRECTIONS, DIMENSIONS AND LOCATIONS ARE APPROXIMATE LEGEND SITE LOCATION 0 800 1,600400 SCALE IN FEET BORING LOCATIONS FIGURE 2PROJECT NO.DATE 2_108153001_BL_93.mxd AOBB-4 TD=16.5 SOURCE: GOOGLE EARTH, 2016. BORING TD=TOTAL DEPTH IN FEET RECYCLED WATER PHASE III PIPELINE SEGMENT 9 PROJECT CARLSBAD, CALIFORNIA1081530016/16 M E X I C OUSAPacific O c e a n SAN JACINTO ELSINORE IM P E RIA L WHITTIER SAN ANDREAS NEW PORT-INGLEWOOD C O R O N A D O B A N K S A N D IE G O T R O U G H SAN CLEMENTE S A N T A C RUZ-SANTA CATALINA RIDGE P A L O S VERDES OFFSHORE ZONE OF DEFORMATIONGARLOCKWHITE WOLFCLEARWATERS A N GABRIEL SIERRA MADRE BANNING MISSION CREEK BLA CK W ATE RHARPER LOCKHART LEN W O O D CAMP ROCK CALIC O LUDLOW PIS GAHBULLION MO U N T AIN JO HNS O N VALLEY E M ERSO N P IN T O M O UN TAINMANIX MIRAGE VALLEY NORTHHELENDALE FRONTAL CHINO S A N J O S ECUCAMON G A MALIBU COAS T SA N T A MONICA SANCAYETANO SANTASUSANASIMI-S A N T A R O S A N O R T H R ID G E C HARN O CK S A W P ITCAN Y O N SUPERSTITION HILLS NEVADA CALIFORNIA R O S E C A NYONSan Bernardino County Kern County Riverside CountySan Diego County Imperial County Los Angeles County V e n t u r a Co u n t y Orange County Riverside CountySan Bernardino CountyL o s A n g e le s Co u n t y Kern CountyIndioIrvine Pomona Mojave Anaheim Barstow Temecula Palmdale El CentroSanDiego Escondido Oceanside SantaAna Riverside Tehachapi Long Beach Wrightwood ChulaVista Los Angeles Victorville SanClemente PalmSprings Big Bear CityThousandOaksSanBernardino LakeArrowhead Twentynine Palms Baker DesertCenter CALIFOR NIA 0 30 60 SCALE IN MILES LEGEND HOLOCENE ACTIVE CALIFORNIA FAULT ACTIVITY HISTORICALLY ACTIVE LATE QUATERNARY (POTENTIALLY ACTIVE) STATE/COUNTY BOUNDARY QUATERNARY (POTENTIALLY ACTIVE) SITE 3_108153001_F_93.mxd AOBNOTE: DIRECTIONS, DIMENSIONS AND LOCATIONS ARE APPROXIMATE. FAULT LOCATIONS FIGURE 3PROJECT NO.DATE SOURCE: JENNINGS, C.W., AND BRYANT, W.A., 2010, FAULT ACTIVITY MAP OF CALIFORNIA, CALIFORNIA GEOLOGICAL SURVEY. RECYCLED WATER PHASE III PIPELINE SEGMENT 9 PROJECT CARLSBAD, CALIFORNIA1081530016/16 SOURCE: KENNEDY, M.P., ET AL, 2007, GEOLOGIC MAP OF THE OCEANSIDE 30' X 60'QUADRANGLE, CALIFORNIA GEOLOGY FIGURE 4PROJECT NO.DATE 4_108153001_G_93.mxd AOBDELMAR FORMATION TORREY SANDSTONE LEGEND VERY OLD PARALIC DEPOSITS, UNIT 10-11Qvop10-11 YOUNG ALLUVIAL FLOODPLAIN DEPOSITSQya Td 0 2,000 4,000 SCALE IN FEET Qvop2-4 VERY OLD PARALIC DEPOSITS, UNIT 13Qvop13 UD FAULT - SOLID WHERE ACCURATELYLOCATED, DASHED WHERE APPROXIMATE, DOTTED WHERE CONCEALED. ARROW AND NUMBER INDICATE DIRECTION AND ANGLE OF DIP OF FAULT PLANE 5 OLD PARALIC DEPOSITS, UNIT 2-4Qop2-4 OLD PARALIC DEPOSITS, UNIT 6-7Qop6-7 Tt STRIKE AND DIP OF BEDS, INCLINED RECYCLED WATER PHASE III PIPELINE SEGMENT 9 PROJECT CARLSBAD, CALIFORNIA1081530016/16 Qpe Qvop10-11 Tsa Q ya LANDSLIDE DEPOISTS, UNDIVIDEDQls PARALIC ESTUARINE DEPOSITSQpe SANTIAGO FORMATIONTsa SITE LOCATION Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc APPENDIX A BORING LOGS Field Procedure for the Collection of Disturbed Samples Disturbed soil samples were obtained in the field using the following method. Bulk Samples Bulk samples of representative earth materials were obtained from the cuttings of the explora- tory borings. The samples were bagged and transported to the laboratory for testing. Field Procedure for the Collection of Relatively Undisturbed Samples Relatively undisturbed soil samples were obtained in the field using a modified split-barrel drive sampler. The sampler, with an external diameter of 3.0 inches, was lined with 1-inch long, thin brass rings with inside diameters of approximately 2.4 inches. The sample barrel was driven into the ground with the weight of a 140-pound hammer, in general accordance with ASTM D 3550. The driving weight was permitted to fall freely. The approximate length of the fall, the weight of the hammer, and the number of blows per foot of driving are presented on the boring logs as an index to the relative resistance of the materials sampled. The samples were removed from the sample barrel in the brass rings, sealed, and transported to the laboratory for testing. 0 5 10 15 20 XX/XX SM CL Bulk sample. Modified split-barrel drive sampler. 2-inch inner diameter split-barrel drive sampler. No recovery with modified split-barrel drive sampler, or 2-inch inner diameter split-barrel drive sampler. Sample retained by others. Standard Penetration Test (SPT). No recovery with a SPT. Shelby tube sample. Distance pushed in inches/length of sample recovered in inches. No recovery with Shelby tube sampler. Continuous Push Sample. Seepage. Groundwater encountered during drilling. Groundwater measured after drilling. MAJOR MATERIAL TYPE (SOIL):Solid line denotes unit change. Dashed line denotes material change. Attitudes: Strike/Dip b: Bedding c: Contact j: Joint f: Fracture F: Fault cs: Clay Seam s: Shear bss: Basal Slide Surface sf: Shear Fracture sz: Shear Zone sbs: Shear Bedding Surface The total depth line is a solid line that is drawn at the bottom of the boring. BORING LOG Explanation of Boring Log Symbols PROJECT NO. DATE FIGUREDEPTH (feet)BulkSAMPLESDrivenBLOWS/FOOTMOISTURE (%)DRY DENSITY (PCF)SYMBOLCLASSIFICATIONU.S.C.S.BORING LOG EXPLANATION SHEET SOIL CLASSIFICATION CHART PER ASTM D 2488 PRIMARY DIVISIONS SECONDARY DIVISIONS GROUP SYMBOL GROUP NAME COARSE- GRAINED SOILS more than 50% retained on No. 200 sieve GRAVEL more than 50% of coarse fraction retained on No. 4 sieve CLEAN GRAVELless than 5% fines GW well-graded GRAVEL GP poorly graded GRAVEL GRAVEL with DUAL CLASSIFICATIONS 5% to 12% fines GW-GM well-graded GRAVEL with silt GP-GM poorly graded GRAVEL with silt GW-GC well-graded GRAVEL with clay GP-GC poorly graded GRAVEL with clay GRAVEL with FINES more than 12% fines GM silty GRAVEL GC clayey GRAVEL GC-GM silty, clayey GRAVEL SAND 50% or more of coarse fraction passes No. 4 sieve CLEAN SAND less than 5% fines SW well-graded SAND SP poorly graded SAND SAND with DUAL CLASSIFICATIONS 5% to 12% fines SW-SM well-graded SAND with silt SP-SM poorly graded SAND with silt SW-SC well-graded SAND with clay SP-SC poorly graded SAND with clay SAND with FINES more than 12% fines SM silty SAND SC clayey SAND SC-SM silty, clayey SAND FINE- GRAINED SOILS 50% or more passes No. 200 sieve SILT and CLAY liquid limit less than 50% INORGANIC CL lean CLAY ML SILT CL-ML silty CLAY ORGANIC OL (PI > 4)organic CLAY OL (PI < 4)organic SILT SILT and CLAY liquid limit 50% or more INORGANIC CH fat CLAY MH elastic SILT ORGANIC OH (plots on or above “A”-line)organic CLAY OH (plots below “A”-line)organic SILT Highly Organic Soils PT Peat USCS METHOD OF SOIL CLASSIFICATION Explanation of USCS Method of Soil Classification PROJECT NO.DATE FIGURE APPARENT DENSITY - COARSE-GRAINED SOIL APPARENT DENSITY SPOOLING CABLE OR CATHEAD AUTOMATIC TRIP HAMMER SPT (blows/foot) MODIFIED SPLIT BARREL (blows/foot) SPT (blows/foot) MODIFIED SPLIT BARREL (blows/foot) Very Loose < 4 < 8 < 3 < 5 Loose 5 - 10 9 - 21 4 - 7 6 - 14 Medium Dense 11 - 30 22 - 63 8 - 20 15 - 42 Dense 31 - 50 64 - 105 21 - 33 43 - 70 Very Dense > 50 > 105 > 33 > 70 CONSISTENCY - FINE-GRAINED SOIL CONSIS-TENCY SPOOLING CABLE OR CATHEAD AUTOMATIC TRIP HAMMER SPT (blows/foot) MODIFIED SPLIT BARREL (blows/foot) SPT (blows/foot) MODIFIED SPLIT BARREL (blows/foot) Very Soft < 2 < 3 < 1 < 2 Soft 2 - 4 3 - 5 1 - 3 2 - 3 Firm 5 - 8 6 - 10 4 - 5 4 - 6 Stiff 9 - 15 11 - 20 6 - 10 7 - 13 Very Stiff 16 - 30 21 - 39 11 - 20 14 - 26 Hard > 30 > 39 > 20 > 26 LIQUID LIMIT (LL), %PLASTICITY INDEX (PI), %0 10 107 4 20 30 40 50 60 70 0 20 30 40 50 60 70 80 90 100 MH or OH ML or OLCL - ML PLASTICITY CHART GRAIN SIZE DESCRIPTION SIEVE SIZE GRAIN SIZE APPROXIMATE SIZE Boulders > 12”> 12”Larger than basketball-sized Cobbles 3 - 12”3 - 12”Fist-sized to basketball-sized Gravel Coarse 3/4 - 3”3/4 - 3”Thumb-sized to fist-sized Fine #4 - 3/4”0.19 - 0.75”Pea-sized to thumb-sized Sand Coarse #10 - #4 0.079 - 0.19”Rock-salt-sized to pea-sized Medium #40 - #10 0.017 - 0.079”Sugar-sized to rock-salt-sized Fine #200 - #40 0.0029 - 0.017” Flour-sized to sugar-sized Fines Passing #200 < 0.0029”Flour-sized and smaller CH or OH CL or OL 0 10 20 30 40 45 51 84 5.8 4.7 106.7 100.8 SM SM ASPHALT CONCRETE:Approximately 6 inches thick. BASE:Approximately 6 inches thick. FILL: Brown, moist, medium dense, silty fine to medium SAND; scattered gravel. OLD PARALIC DEPOSITS:Dark yellowish brown, moist, medium dense, silty fine SAND; micaceous; cohesionless. Yellowish brown. Light brown. Dense. Total Depth = 16.5 feet. Groundwater not encountered. Backfilled and patched with perma patch shortly after drilling on 5/17/16. Note: Groundwater, though not encountered at the time of drilling, may rise to a higher level due to seasonal variations in precipitation and several other factors as discussed in the report. The ground elevation shown above is an estimation only. It is based on our interpretations of published maps and other documents reviewed for the purposes of this evaluation. It is not sufficiently accurate for preparing construction bids and design documents. BORING LOG RECYCLED WATER PHASE III PIPELINE SEGMENT 9 PROJECT CARLSBAD, CALIFORNIA PROJECT NO. 108153001 DATE 6/16 FIGURE A-1DEPTH (feet)BulkSAMPLESDrivenBLOWS/FOOTMOISTURE (%)DRY DENSITY (PCF)SYMBOLCLASSIFICATIONU.S.C.S.DESCRIPTION/INTERPRETATION DATE DRILLED 5/17/16 BORING NO.B-1 GROUND ELEVATION 64'  (MSL)SHEET 1 OF METHOD OF DRILLING 8" Diameter Hollow Stem Auger (A-300) (Scott's Drilling) DRIVE WEIGHT 140 lbs. (Cathead)DROP 30" SAMPLED BY CAT LOGGED BY CAT REVIEWED BY TCS 1 0 10 20 30 40 44 88 50/4" 5.7 10.1 117.3 123.4 SM SM ASPHALT CONCRETE:Approximately 3 inches thick (no base). FILL:Dark brown, moist, medium dense, silty fine SAND; scattered gravel. Few pockets of clay.Scattered brick fragments. OLD PARALIC DEPOSITS:Grayish brown, moist to wet, medium dense, silty fine to medium SAND; clayey; some yellow staining. Dense; gravelly. Dark yellowish brown; fine to coarse sand; no clay. Light gray; very dense; fine sand. Total Depth = 15.9 feet. Groundwater not encountered. Backfilled and patched with perma patch shortly after drilling on 5/17/16. Note: Groundwater, though not encountered at the time of drilling, may rise to a higher level due to seasonal variations in precipitation and several other factors as discussed in the report. The ground elevation shown above is an estimation only. It is based on our interpretations of published maps and other documents reviewed for the purposes of this evaluation. It is not sufficiently accurate for preparing construction bids and design documents. BORING LOG RECYCLED WATER PHASE III PIPELINE SEGMENT 9 PROJECT CARLSBAD, CALIFORNIA PROJECT NO. 108153001 DATE 6/16 FIGURE A-2DEPTH (feet)BulkSAMPLESDrivenBLOWS/FOOTMOISTURE (%)DRY DENSITY (PCF)SYMBOLCLASSIFICATIONU.S.C.S.DESCRIPTION/INTERPRETATION DATE DRILLED 5/17/16 BORING NO.B-2 GROUND ELEVATION 42'  (MSL)SHEET 1 OF METHOD OF DRILLING 8" Diameter Hollow Stem Auger (A-300) (Scott's Drilling) DRIVE WEIGHT 140 lbs. (Cathead)DROP 30" SAMPLED BY CAT LOGGED BY CAT REVIEWED BY TCS 1 0 10 20 30 40 90 56 66 4.0 3.5 115.1 106.1 SM SM ASPHALT CONCRETE:Approximately 3-1/2 inches thick. BASE:Approximately 2 inches thick. FILL: Reddish brown, moist, medium dense, silty fine to medium SAND. OLD PARALIC DEPOSITS:Reddish brown, moist, dense, silty fine SAND; scattered pinhole voids. Yellowish brown; medium dense; fine to medium sand. Light yellowish brown; fine sand.Fine to coarse sand with gravel up to 1/2 inch. Total Depth = 16.5 feet. Groundwater not encountered. Backfilled and patched with perma patch shortly after drilling on 5/17/16. Note: Groundwater, though not encountered at the time of drilling, may rise to a higher level due to seasonal variations in precipitation and several other factors as discussed in the report. The ground elevation shown above is an estimation only. It is based on our interpretations of published maps and other documents reviewed for the purposes of this evaluation. It is not sufficiently accurate for preparing construction bids and design documents. BORING LOG RECYCLED WATER PHASE III PIPELINE SEGMENT 9 PROJECT CARLSBAD, CALIFORNIA PROJECT NO. 108153001 DATE 6/16 FIGURE A-3DEPTH (feet)BulkSAMPLESDrivenBLOWS/FOOTMOISTURE (%)DRY DENSITY (PCF)SYMBOLCLASSIFICATIONU.S.C.S.DESCRIPTION/INTERPRETATION DATE DRILLED 5/17/16 BORING NO.B-3 GROUND ELEVATION 46'  (MSL)SHEET 1 OF METHOD OF DRILLING 8" Diameter Hollow Stem Auger (A-300) (Scott's Drilling) DRIVE WEIGHT 140 lbs. (Cathead)DROP 30" SAMPLED BY CAT LOGGED BY CAT REVIEWED BY TCS 1 0 10 20 30 40 27 54 57 7.3 8.5 97.7 119.7 SM SM ASPHALT CONCRETE:Approximately 4 inches thick. BASE:Approximately 5 inches thick. FILL: Reddish brown, moist, medium dense, silty fine to medium SAND; few gravel.@ 2': Gray; fine to coarse sand.@ 2.5': Reddish brown; fine to medium sand.Brown; trace coarse sand and fine gravel. OLD PARALIC DEPOSITS:Reddish brown, moist, medium dense, silty fine to medium SAND; trace clay. Some light brown mottling. Total Depth = 16.5 feet. Groundwater not encountered. Backfilled and patched with perma patch shortly after drilling on 5/17/16. Note: Groundwater, though not encountered at the time of drilling, may rise to a higher level due to seasonal variations in precipitation and several other factors as discussed in the report. The ground elevation shown above is an estimation only. It is based on our interpretations of published maps and other documents reviewed for the purposes of this evaluation. It is not sufficiently accurate for preparing construction bids and design documents. BORING LOG RECYCLED WATER PHASE III PIPELINE SEGMENT 9 PROJECT CARLSBAD, CALIFORNIA PROJECT NO. 108153001 DATE 6/16 FIGURE A-4DEPTH (feet)BulkSAMPLESDrivenBLOWS/FOOTMOISTURE (%)DRY DENSITY (PCF)SYMBOLCLASSIFICATIONU.S.C.S.DESCRIPTION/INTERPRETATION DATE DRILLED 5/17/16 BORING NO.B-4 GROUND ELEVATION 99'  (MSL)SHEET 1 OF METHOD OF DRILLING 8" Diameter Hollow Stem Auger (A-300) (Scott's Drilling) DRIVE WEIGHT 140 lbs. (Cathead)DROP 30" SAMPLED BY CAT LOGGED BY CAT REVIEWED BY TCS 1 Recycled Water Phase III, Pipeline Segment 9 Project June 14, 2016 Carlsbad, California Project No. 108153001 108153001 R.doc APPENDIX B LABORATORY TESTING Classification Soils were visually and texturally classified in accordance with the Unified Soil Classification System (USCS) in general accordance with ASTM D 2488. Soil classifications are indicated on the logs of the exploratory borings in Appendix A. In-Place Moisture and Density Tests The moisture content and dry density of relatively undisturbed samples obtained from the ex- ploratory borings were evaluated in general accordance with ASTM D 2937. The test results are presented on the logs of the exploratory borings in Appendix A. Gradation Analysis Gradation analysis tests were performed on selected representative soil samples in general accord- ance with ASTM D 422. The grain-size distribution curves are shown on Figures B-1 through B-3. The test results were utilized in evaluating the soil classifications in accordance with the USCS. Direct Shear Tests Direct shear tests were performed on representative samples in general accordance with ASTM D 3080 to evaluate the shear strength characteristics of the selected material. The samples were inundated during shearing to represent adverse field conditions. The test results are shown on Figures B-4 and B-5. Soil Corrosivity Tests Soil pH and electrical resistivity tests were performed on representative samples in general ac- cordance with CT 643. The chloride contents of the selected samples were evaluated in general accordance with CT 422. The sulfate contents of the selected samples were evaluated in general accordance with CT 417. The test results are presented on Figure B-6. Coarse Fine Coarse Medium SILT CLAY 3" 2"¾"½" ⅜"4 8 3050 PERFORMED IN GENERAL ACCORDANCE WITH ASTM D 422 USCS -- D60 SM-- -- -- 12 Passing No. 200 (%) CcCu B-1 4.0-8.0 -- -- -- -- GRAVEL SAND FINES Symbol Plasticity Index Plastic Limit Liquid Limit 1½" 1" Depth (ft)D30 Fine Sample Location 100 D10 16 200 108153001 6/16 B-1RECYCLED WATER PHASE III PIPELINE SEGMENT 9 PROJECT CARLSBAD, CALIFORNIA 0.0 10.0 20.0 30.0 40.0 50.0 60.0 70.0 80.0 90.0 100.0 0.00010.0010.010.1110100PERCENT FINER BY WEIGHTGRAIN SIZE IN MILLIMETERS U.S. STANDARD SIEVE NUMBERS HYDROMETER GRADATION TEST RESULTS PROJECT NO. DATE FIGURE 108153001_SIEVE B-1 @ 4.0-8.0.xls Coarse Fine Coarse Fine Silt Clay 3" 1-1/2" 1" 3/4" 1/2" 3/8" 4 8 16 30 50 100 200 PERFORMED IN GENERAL ACCORDANCE WITH ASTM D 422 Symbol Plasticity Index Plastic Limit Liquid Limit Depth (ft)CcCu USCSD60 Medium GRAVEL SAND FINES D30D10 Passing No. 200 (%) Sample Location B-2 2.0-5.0 -- -- -- -- -- -- -- -- 19 SM RECYCLED WATER PHASE III B-2PIPELINE SEGMENT 9 PROJECT 108153001 6/16 CARLSBAD, CALIFORNIA 0 10 20 30 40 50 60 70 80 90 100 0.00010.0010.010.1110100PERCENT FINER BY WEIGHTGRAIN SIZE IN MILLIMETERS U.S. STANDARD SIEVE NUMBERS HYDROMETER GRADATION TEST RESULTS PROJECT NO. DATE FIGURE 108153001_SIEVE B-2 @ 2.0-5.0.xls Coarse Fine Coarse Medium SILT CLAY 3" 2"¾"½" ⅜"4 8 3050 PERFORMED IN GENERAL ACCORDANCE WITH ASTM D 422 USCS -- D60 SM-- -- -- 22 Passing No. 200 (%) CcCu B-4 5.0-6.5 -- -- -- -- GRAVEL SAND FINES Symbol Plasticity Index Plastic Limit Liquid Limit 1½" 1" Depth (ft)D30 Fine Sample Location 100 D10 16 200 108153001 6/16 B-3RECYCLED WATER PHASE III PIPELINE SEGMENT 9 PROJECT CARLSBAD, CALIFORNIA 0.0 10.0 20.0 30.0 40.0 50.0 60.0 70.0 80.0 90.0 100.0 0.00010.0010.010.1110100PERCENT FINER BY WEIGHTGRAIN SIZE IN MILLIMETERS U.S. STANDARD SIEVE NUMBERS HYDROMETER GRADATION TEST RESULTS PROJECT NO. DATE FIGURE 108153001_SIEVE B-4 @ 5.0-6.5.xls X 6/16 PIPELINE SEGMENT 9 PROJECT RECYCLED WATER PHASE III CARLSBAD, CALIFORNIA Ultimate5.0-6.5B-1 B-4 PERFORMED IN GENERAL ACCORDANCE WITH ASTM D 3080 Silty SAND 108153001 Cohesion, c (psf) Friction Angle,  (degrees)Soil Type SM33 40 0 SM Description Symbol Sample Location 0 Depth (ft) Shear Strength 5.0-6.5Silty SAND B-1 Peak 0 1000 2000 3000 4000 0 1000 2000 3000 4000SHEAR STRESS (PSF)NORMAL STRESS (PSF) DIRECT SHEAR TEST RESULTS PROJECT NO. DATE FIGURE 108153001_DIRECT SHEAR B-1 @ 5.0-6.5.xls X 6/16 PIPELINE SEGMENT 9 PROJECT RECYCLED WATER PHASE III CARLSBAD, CALIFORNIA Ultimate5.0-6.5B-3 B-5 PERFORMED IN GENERAL ACCORDANCE WITH ASTM D 3080 Silty SAND 108153001 Cohesion, c (psf) Friction Angle,  (degrees)Soil Type SM32 38 0 SM Description Symbol Sample Location 0 Depth (ft) Shear Strength 5.0-6.5Silty SAND B-3 Peak 0 1000 2000 3000 4000 0 1000 2000 3000 4000SHEAR STRESS (PSF)NORMAL STRESS (PSF) DIRECT SHEAR TEST RESULTS PROJECT NO. DATE FIGURE 108153001_DIRECT SHEAR B-3 @ 5.0-6.5.xls 1 PERFORMED IN GENERAL ACCORDANCE WITH CALIFORNIA TEST METHOD 643 2 PERFORMED IN GENERAL ACCORDANCE WITH CALIFORNIA TEST METHOD 417 3 PERFORMED IN GENERAL ACCORDANCE WITH CALIFORNIA TEST METHOD 422 108153001 140 90 65 18,000 2.0-5.0 3,300 5.0-10.0 B-3 B-4 CHLORIDE CONTENT 3 (ppm) pH 1SAMPLE DEPTH (FT) SAMPLE LOCATION (Ohm-cm) RESISTIVITY 1 SULFATE CONTENT 2 (%)(ppm) B-1 5,900 4.0-8.0 7.1 7.0 6.9 6/16 B-6RECYCLED WATER PHASE III PIPELINE SEGMENT 9 PROJECT CARLSBAD, CALIFORNIA 0.009 0.005 20 0.002 90 50 CORROSIVITY TEST RESULTS PROJECT NO. DATE FIGURE 108153001_CORROSIVITY Page 1.xls