4360 - Water Research Foundation
Transcription
4360 - Water Research Foundation
Acoustic Signal Processing for Pipe Condition Assessment Web Report #4360 Subject Area: Infrastructure About the Water Research Foundation The Water Research Foundation (WRF) is a member-supported, international, 501(c)3 nonprofit organization that sponsors research that enables water utilities, public health agencies, and other professionals to provide safe and affordable drinking water to consumers. WRF’s mission is to advance the science of water to improve the quality of life. To achieve this mission, WRF sponsors studies on all aspects of drinking water, including resources, treatment, and distribution. Nearly 1,000 water utilities, consulting firms, and manufacturers in North America and abroad contribute subscription payments to support WRF’s work. Additional funding comes from collaborative partnerships with other national and international organizations and the U.S. federal government, allowing for resources to be leveraged, expertise to be shared, and broad-based knowledge to be developed and disseminated. From its headquarters in Denver, Colorado, WRF’s staff directs and supports the efforts of more than 800 volunteers who serve on the board of trustees and various committees. These volunteers represent many facets of the water industry, and contribute their expertise to select and monitor research studies that benefit the entire drinking water community. Research results are disseminated through a number of channels, including reports, the Website, Webcasts, workshops, and periodicals. WRF serves as a cooperative program providing subscribers the opportunity to pool their resources and build upon each other’s expertise. By applying WRF research findings, subscribers can save substantial costs and stay on the leading edge of drinking water science and technology. Since its inception, WRF has supplied the water community with more than $460 million in applied research value. More information about WRF and how to become a subscriber is available at http://www.waterrf.org. ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Acoustic Signal Processing for Pipe Condition Assessment Prepared by: Peter Paulson and Roberto Mascarenhas Pure Technologies, Ltd.,1050, 340 12 Avenue SW, Calgary, AB T2R 1L5 Canada and Graham E.C. Bell and Brien Clark HDR|Schiff, 431 West Baseline Road, Claremont, CA 91711 Sponsored by: U.S. Environmental Protection Agency 26 West Martin Luther King Drive, Cincinnati, OH 45268 Water Environment Research Foundation 635 Slater’s Lane, G-110, Alexandria, VA 22314 and Water Research Foundation 6666 West Quincy Avenue, Denver, CO 80235 Published by: ©2014 Water Research Foundation. ALL RIGHTS RESERVED. DISCLAIMER This study was funded by the U.S. Environmental Protection Agency (EPA), the Water Environment Research Foundation (WERF), and the Water Research Foundation (WRF) under Cooperative Agreement No. CR-83419201. EPA, WERF, and WRF assume no responsibility for the content of the research study reported in this publication or for the opinions or statements of fact expressed in the report. The mention of trade names for commercial products does not represent or imply the approval or endorsement of EPA, WERF, or WRF. This report is presented solely for informational purposes. Copyright © 2014 by Water Research Foundation ALL RIGHTS RESERVED. No part of this publication may be copied, reproduced or otherwise utilized without permission. Printed in the U.S.A. ©2014 Water Research Foundation. ALL RIGHTS RESERVED. CONTENTS LIST OF FIGURES ..................................................................................................................... VII FOREWORD……... ..................................................................................................................... XI ACKNOWLEDGMENTS ......................................................................................................... XIII EXECUTIVE SUMMARY .........................................................................................................XV CHAPTER 1: BACKGROUND INFORMATION AND PROJECT MOTIVATION .................. 1 Condition Assessment vs. Condition Monitoring ............................................................... 3 PCCP Pipe Material Characteristics ................................................................................... 3 How PCCP Fails ................................................................................................................. 4 Condition Assessment of PCCP.......................................................................................... 5 Internal Visual Inspection and Aural Sounding ...................................................... 5 Impact Echo ............................................................................................................ 5 Electromagnetic Inspection ..................................................................................... 5 Acoustic Monitoring of PCCP ............................................................................................ 6 Principals and Foundation....................................................................................... 6 Methodologies and History of Use ......................................................................... 6 Problem Statement: Passive Condition Assessment of PCCP by Processing Acoustic Data to Mine Information Condition Assessment Information from Condition Monitoring Signals.................................................................................................. 9 Extension of PCCP Concepts to Pipe Wall Assessment for other pipe materials ............ 11 CHAPTER 2: LITERATURE SURVEY ON RESEARCH TOPICS .......................................... 13 Background on Acoustics, Sounds and Signals ................................................................ 13 Acoustic, Emission, Monitoring and Sounds of PCCP..................................................... 15 Current State of Condition Assessment for PCCP ............................................................ 16 Current State of Acoustic Signal Processing as Applied to PCCP ................................... 17 Other Candidate Techniques for Processing Acoustic Signals from PCCP Wire Breaks ............................................................................................................................... 20 Time Domain Pattern or Characteristic Analysis ............................................................. 21 Power and Energy (Amplitude) Signal Information ............................................. 21 Time Between Wire Breaks (Wire Reliability) .................................................... 21 Feature Extraction and Analysis Methods ........................................................................ 22 Fourier Transforms ............................................................................................... 22 Wavelet Transforms .............................................................................................. 23 Dissimilarities Between Fourier and Wavelet Transforms ................................... 23 Monte Carlo Techniques for Signal Processing.................................................... 24 Pipe Wall Assessment for Other Pipe Materials ............................................................... 25 Summary of the Literature ................................................................................................ 25 v ©2014 Water Research Foundation. ALL RIGHTS RESERVED. CHAPTER 3: EXPERIMENTAL SET-UPS, TESTING PROCEDURES, AND DATA MINING REPOSITORY ............................................................................................. 27 Passive Condition Assessment of PCCP Facility ............................................................. 27 Design of the Facility of PCA-PCCP Facility ...................................................... 27 Instrumentation Description.................................................................................. 32 Test Procedures ..................................................................................................... 34 Pipe Wall Assessment DIP Facility .................................................................................. 36 Design of the Facility ............................................................................................ 36 Description of Instrumentation ............................................................................. 36 Test Procedures ..................................................................................................... 37 Existing In-Situ Monitoring Systems................................................................................ 37 Overview of Monitoring Systems ......................................................................... 37 Participant Support................................................................................................ 38 Participant Monitoring Systems ............................................................................ 39 CHAPTER 4: RESULTS AND SIGNAL ANALYSIS FOR PCA PCCP DATA ....................... 43 Presentation of Acoustic Test Data ................................................................................... 43 Observations and Analysis of PCCP Test Data .................................................... 44 Analysis Methods.............................................................................................................. 47 Short-Time Fourier Transform ............................................................................. 48 Wavelet Analysis .................................................................................................. 48 Monte Carlo Analysis ........................................................................................... 48 Application of Best Candidate Analysis Method to Real World Data ............................. 48 Selected Data ........................................................................................................ 48 Characteristics and Comparison of Results .......................................................... 49 CHAPTER 5: PIPE WALL ASSESSMENT (NON-PCCP) RESULTS ...................................... 59 Presentation and Analysis of PWA Test Data .................................................................. 59 CHAPTER 6: SUMMARY AND CONCLUSIONS OF THE RESEARCH ............................... 61 CHAPTER 7: FUTURE RESEARCH SUGGESTIONS.............................................................. 63 REFERENCES ............................................................................................................................ 65 BIBLIOGRAPHY………………………………………………………………………………..69 ABBREVIATIONS ...................................................................................................................... 71 vi ©2014 Water Research Foundation. ALL RIGHTS RESERVED. LIST OF FIGURES 1.1: PCCP failure ............................................................................................................................ 1 1.2: LCP .......................................................................................................................................... 3 1.3: ECP .......................................................................................................................................... 3 1.4: Wire breaks lead to PCCP failure ............................................................................................ 4 1.5: PCCP management cycle ......................................................................................................... 5 1.6: Live deployment of a fiber optic cable .................................................................................... 6 1.7: Wet AFO deployment insertion stack ...................................................................................... 7 1.8: How many wire breaks are too many?..................................................................................... 7 1.9: Example of PWA using a moving sensor .............................................................................. 11 2.1: Pluck of a guitar string showing characteristic attack and decay .......................................... 14 2.2: Striking of a cymbal showing characteristic attack and decay. ............................................. 14 2.3: Typical wire break ................................................................................................................. 15 2.4: Integrated power spectral density of first normalized acoustic event days prior to failure .......................................................................................................... 18 2.5: Integrated PSD of normalized sub-event in acoustic event less than an hour before failure............................................................................................................. 18 2.6: Aboveground PCCP instrumented with strain gages and displacement monitoring physical scales ................................................................................................ 19 2.7: Fourier basis functions, time-frequency tiles, and coverage of the time-frequency plane. ....................................................................................................... 24 2.8: Daubechies wavelet basis functions, time-frequency tiles, and coverage of the time-frequency plane. ............................................................................................. 24 3.1: Engineering drawing of test set-up ........................................................................................ 28 3.2: Pipe burial site map................................................................................................................ 29 vii ©2014 Water Research Foundation. ALL RIGHTS RESERVED. 3.3(a): End plate with 2-inch tap, (b): End plate with 1-inch tap ................................................. 30 3.4: Crane-lifted PCCP ................................................................................................................. 31 3.5: PCCP stake positions ............................................................................................................. 31 3.6(a): Exposed pipe ends and pits, (b): Pit window with exposed prestressing wire .................. 32 3.7(a): Fiber insertion at pipe end, (b): Fiber splicing, (c): Impact testing for AFO system ........ 32 3.8(a): Constant pressure device at pipe end, (b): Water reservoir ............................................... 33 3.9: Volume of water added vs. number of sequential wire cuts .................................................. 34 3.10: Bolt cutters used to simulate wire breaks ............................................................................ 35 3.11: Wires cut in a systematic fashion ........................................................................................ 35 3.12: Onsite workstation ............................................................................................................... 35 3.13: Orientation of the buried PCCP test facility ........................................................................ 35 3.14(a): 12-inch ductile iron pipe, (b): Buried with earth displaced from PCCP test ................... 36 3.15(a): Various joint connections, (b): Addition of up to six (6) additional clamps ................... 36 3.16: Example of test procedure ................................................................................................... 37 3.17: Excavation of Howard County's 36-inch southwestern transmission main......................... 39 3.18: Damage to WSSC's 96-inch Potomac transmission main ................................................... 40 4.1: Fiber sensor raw signal from experimental test site wire cut ................................................ 43 4.2: Fiber sensor and hydrophone data ......................................................................................... 44 4.3: Pipe yard wire cut data........................................................................................................... 45 4.4: MCUA wire cut data .............................................................................................................. 45 4.5: Pipe yard wire cut frequency ratio vs. wire cut ..................................................................... 46 4.6: MCUA wire cut frequency ratio vs. wire cut......................................................................... 46 4.7: Measured acoustic output as a function of wire cuts ............................................................. 47 4.8: RMS average acoustic power vs. remaining wires ................................................................ 47 4.9: Average RMS power from pipe yard D2 ............................................................................... 49 viii ©2014 Water Research Foundation. ALL RIGHTS RESERVED. 4.10: Average RMS power from pipe yard D2 with all cuts ........................................................ 50 4.11: Average RMS power from pipe yard D3 ............................................................................. 51 4.12: RMS power from pipe yard D2 and D3 ............................................................................... 51 4.13: Average RMS power from WSSC AFO site ....................................................................... 52 4.14: Average RMS power from Ottawa AFO site....................................................................... 53 4.15: Average RMS power from San Diego AFO site ................................................................. 53 4.16: Average RMS power from Tucson AFO site ...................................................................... 54 4.17: Average RMS power from Cutzamala AFO site ................................................................. 54 4.18: HEMP analysis from pipe yard D2 ...................................................................................... 56 4.19: HEMP analysis from pipe yard D3 ...................................................................................... 56 4.20: HEMP analysis from WSSC AFO site ................................................................................ 57 4.21: HEMP analysis from Ottawa AFO site................................................................................ 57 4.22: HEMP analysis from San Diego AFO site .......................................................................... 58 4.23: HEMP analysis from Tucson AFO site ............................................................................... 58 5.1: Pipe wall assessment data with various pipe joint connections ............................................. 59 5.2: Pipe wall assessment data, illustrating effect of additional clamps ....................................... 60 ix ©2014 Water Research Foundation. ALL RIGHTS RESERVED. ©2014 Water Research Foundation. ALL RIGHTS RESERVED. FOREWORD The Water Research Foundation (Foundation) is a nonprofit corporation dedicated to the development and implementation of scientifically sound research designed to help drinking water utilities respond to regulatory requirements and address high-priority concerns. The Foundation’s research agenda is developed through a process of consultation with Foundation subscribers and other drinking water professionals. The Foundation’s Board of Trustees and other professional volunteers help prioritize and select research projects for funding based upon current and future industry needs, applicability, and past work. The Foundation sponsors research projects through the Focus Area, Emerging Opportunities, and Tailored Collaboration programs, as well as various joint research efforts with organizations such as the U.S. Environmental Protection Agency and the U.S. Bureau of Reclamation. This publication is a result of a research project fully funded or funded in part by Foundation subscribers. The Foundation’s subscription program provides a cost-effective and collaborative method for funding research in the public interest. The research investment that underpins this report will intrinsically increase in value as the findings are applied in communities throughout the world. Foundation research projects are managed closely from their inception to the final report by the staff and a large cadre of volunteers who willingly contribute their time and expertise. The Foundation provides planning, management, and technical oversight and awards contracts to other institutions such as water utilities, universities, and engineering firms to conduct the research. A broad spectrum of water supply issues is addressed by the Foundation's research agenda, including resources, treatment and operations, distribution and storage, water quality and analysis, toxicology, economics, and management. The ultimate purpose of the coordinated effort is to assist water suppliers to provide a reliable supply of safe and affordable drinking water to consumers. The true benefits of the Foundation’s research are realized when the results are implemented at the utility level. The Foundation's staff and Board of Trustees are pleased to offer this publication as a contribution toward that end. Denise L. Kruger Chair, Board of Trustees Water Research Foundation Robert C. Renner, P.E. Executive Director Water Research Foundation xi ©2014 Water Research Foundation. ALL RIGHTS RESERVED. ©2014 Water Research Foundation. ALL RIGHTS RESERVED. ACKNOWLEDGMENTS The authors of this report are grateful to the following water agencies for their cooperation and participation in this project: Arizona Public Service Company Central Arizona Project City of Calgary City of London Dallas Water Utilities Howard County Department of Public Works Louisville Water Company Metropolitan Water District of Southern California Providence Water San Diego County Water Authority Tarrant Regional Water District Tucson Water Washington Suburban Sanitary Commission The authors would also like to thank the members of the Project Advisory Committee for their support and assistance: Randy Randolph, Central Arizona Project David Hughes, American Water Daryl Little, Bureau of Reclamation Jeffrey Yang, U.S. Environmental Protection Agency (EPA) Frank Blaha, WRF Project Manager The authors of this report are indebted to the following individuals whose voluntary assistance made the report possible: Bethany McDonald, John Plattsmier, Cliff Moore, John Galleher, Jr., Mark Holley, Ryan Kraayvanger, Xiangjie Kong, Ali Alavinasab, Brian Lima, Daniel Davis, Stewart Bay, Michael Livermore, Nabil Alfagi, Mark Webb, Adam Koebel, Catalina Goez, Muthu Chandrasekaran, Jack Elliott, Fathalla Gheryani, Hashaon Zwawa, and Nathan Faber. xiii ©2014 Water Research Foundation. ALL RIGHTS RESERVED. ©2014 Water Research Foundation. ALL RIGHTS RESERVED. EXECUTIVE SUMMARY OBJECTIVES This project was designed to improve acoustic signal processing for pipe condition assessment in an experimental environment, which includes burial, pressurization, and subsequent intentional damage to the pre-stressing wires in three specimens of prestressed concrete cylinder pipe (PCCP). BACKGROUND Current acoustic fiber optic (AFO) monitoring can supply a PCCP owner with sufficient warning to avoid a pipeline failure, but only if the information supplied by AFO is used to initiate an emergency pipeline shutdown fairly quickly. Unique to PCCP, individual wire breaks create an excitation in the pipe wall that may vary in response to the remaining compression of the pipe core. In non-PCCP, the structural excitation would require an external source acoustic pulse, causing a response indicative of relative pipe wall stiffness. The purpose of this project is to further research acoustic signal processing to advance the use of this AFO technology for pipe condition assessment. APPROACH The project steps were as follows: 1) Conducted a literature search for relevant past investigations and data mining and processing methodologies 2) Performed a series of tests on a buried PCCP pipe to collect controlled acoustic data as the pipe’s pre-stressing compressive load was removed 3) Evaluated data collected using advanced and emerging data mining and processing methodologies 4) Applied data mining techniques to Pure Technologies’ acoustic fiber optic (AFO) wire break database to identify pipes at varying distress levels 5) Validated the results using data collected from pipes of participating utilities RESULTS/CONCLUSIONS The experimental data was analyzed for average RMS power and peak frequency (HEMP) analysis. While the HEMP analysis did not prove useful, the average RMS power showed promise for correlating the signal amplitude with the number of broken wires. Extending the research to non-PCCP ensured applicability to the broadest possible group of WRF subscribers. A second test setup examined the correlation of acoustic signal response and hoop stiffness of a ductile iron pipe (DIP). The results showed that areas of increased stiffness were discernible from other areas. The ability to successfully distinguish between areas of varying stiffness may be useful in identifying areas of uniform (i.e., general) metal loss in in-service pipe, as these areas would appear as sections of diminished stiffness. xv ©2014 Water Research Foundation. ALL RIGHTS RESERVED. APPLICATIONS/RECOMMENDATIONS For PCCP owners, this research is retrospectively and immediately applicable to AFO monitored water and wastewater pipes. As an optimal result, PCCP owners would extend and improve the service life and operating performance of their critical pipeline assets, ultimately saving significant funds that would otherwise be used in a capital replacement program. RESEARCH PARTNERS U.S. Environmental Protection Agency Water Environment Research Foundation xvi ©2014 Water Research Foundation. ALL RIGHTS RESERVED. CHAPTER 1: BACKGROUND INFORMATION AND PROJECT MOTIVATION All pipelines have a finite useful life. Failure of water pipelines can be sensational. In particular, failure of prestressed concrete cylinder pipe (PCCP) often results in the destruction of housing, buildings and/or roads while simultaneously flooding the surrounding areas, sometimes at a multi-million dollar repair cost to the owner. Even more expensive pipeline replacement or rehabilitation projects costing millions or even billions of dollars can follow (Galleher 2008, Essamin et al. 2005). Further, these failures can wash out parallel sanitary sewers, which can destroy properties and present a public health problem due to possible contamination of drinking water supply (Henry et al. 2005, Ortega et al. 2005). More difficult to quantify are the political and societal costs that accompany being the feature story on national news or local newspapers (Shaver 2009, Gaewski and Blaha 2007). The potential consequences of a PCCP failure incentivize PCCP owners to assess the performance, Figure 1.1: PCCP failure condition and risk of failure of their PCCP Source: SDCWA systems (Romer and Bell 2005, Romer et al. 2008, Bell 2001, Galleher and Stift 1998, Marshall et al. 2005, Ojdrovic et al. 2001, Parks et al. 2001, Zarghamee et al. 1998). Figure 1.1 shows a PCCP pipeline following rupture. PCCP owners need to know, at any given time, whether their pipes are at the beginning, middle or nearing the end of their useful life, and whether significant changes in pipe condition are occurring. Pipes with wire break quantities sufficient to exceed their structural capacity under normal operation or during surge events are near or at the end of their useful life. The obvious next steps in the direction of a commercially available acoustic fiber optic (AFO) monitoring system that can establish both baseline structural condition and on-going loss of core compression are: 1. 2. 3. 4. Collection of AFO monitoring data on a buried PCCP under controlled conditions Selection of the appropriate acoustic data analysis technique Extraction of the key condition information from the data Development of algorithm(s) correlating the number of pre-exiting wire breaks on a pipe to specific acoustic characteristics detected as each wire breaks 5. Testing of the algorithm(s) on utility participant data 6. Validation on utility participant pipelines where possible The primary goal of this project is determine the ability of recently available monitoring technology to determine the current condition of PCCP. Every PCCP owner dreads the possibility of a PCCP failure creating hazard, interrupting service, ballooning budgets, and focusing public 1 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. attention on pipeline operation and maintenance programs. Current AFO monitoring can supply a PCCP owner with sufficient warning to avoid a pipeline failure, but only if the information supplied by AFO is used to initiate an emergency pipeline shut down extremely quickly. In lateJune 2010, the Washington Suburban Sanitary Commission (WSSC) 96-inch Potomac Transmission Main began experiencing wire breaks in rapid succession. Pure Technologies quickly identified the location of the wire breaks using a preinstalled AFO monitoring system. WSSC was notified of the rapid structural deterioration of the pipeline. WSSC initiated an emergency shutdown of the pipeline going into the July 4th weekend, avoided failure and was actually heralded on the local news channel for its proactive measures (Hudson 2010). Excavation of the suspect pipe revealed physical evidence of advanced structural deterioration. The story does not always have this happy ending. In 2006, AFO detected multiple wire breaks on a 66-inch San Diego County Water Authority (SDCWA) PCCP pipeline that had recently been shut down, dewatered and recommissioned in conjunction with installation of the AFO system. Unfortunately, a lag in acoustic data analysis and reporting, and slow data transmission combined to delay delivery of wire break events and locations to the Water Authority. Two months after the pipeline was recommissioned, the pipeline failed catastrophically after 18 wire breaks occurred in the day preceding the failure. The Water Authority was notified of AFOdetected wire breaks near the eventual failure two to three days prior, but did not take action because the baseline wire breaks detected by electromagnetic inspection plus the newly reported AFO-detected wire breaks was still not sufficient to bring the pipeline near failure (Galleher et al. 2007b). However, if the AFO monitoring signals could have been quickly analyzed over the 2 month period to provide not only wire break data, but also condition data in the immediate vicinity of the wire breaks, the Water Authority could have had more time to act. PCCP owners know depressurizing, dewatering, refilling, and repressurizing a pipeline for inspection or repairs causes wear and tear on the pipe. In 2006 the City of Phoenix experienced a catastrophic failure of the 60-inch PCCP Superior Pipeline. The pipeline was repaired and put back into service in 2007 with an AFO monitoring system installed. A phased recommissioning plan was implemented to gradually increase pressure in the hope of avoiding unnecessary wire breaks and structural damage. Despite these efforts wire break activity peaked on startup at relatively low pressure of 20 pounds per square inch (psi) or less, and then again when the pressure was increased from 70 to 90 psi, based on data provided by the City of Phoenix. A wet-deployed AFO monitoring system may ultimately allow PCCP owners to avoid the stress a shutdown places on a pipeline, while still providing actionable baseline condition data and ongoing wire break locations. Combined with structural analysis, this could provide PCCP owners a method for making repair or replace decisions. The purpose of this project is to further research in acoustic signal processing to advance the use of this technology for pipe condition assessment. In particular, this includes the previous work by Bell et al. (2009) for PCCP. The foundation of the research is in the historical practice of using internal inspection of an empty PCCP pipe to sound, hammer or “bong” (mechanical excitation) the interior surfaces of pipe and listening (response signal) using the human ear for “hollow”, “punky” or dull sounds. Changes from the familiar “ringing” sound of the “good” pipe are used as the discriminator for the signal (Gallaher and Stift 1998, Bell et al. 2009). The concept is that the energy released from a wire break is similar to a hammer strike and the coupling between the incompressible fluid (water) and the pipe allows the energy/signal to 2 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. transmit and the response to be received by hydrophones or other acoustic sensors (Konyalian 2005). CONDITION ASSESSMENT VS. CONDITION MONITORING Condition assessment of pipelines is critical to the long-term operational cost and safety of aging pipelines. Knowledge of a pipe’s condition, load bearing capacity, and remaining life is the primary goal of any strategy of a pipeline diagnostic/prognostic system. Damage in pipe will alter the stiffness, mass, or energy dissipation properties of a system, which in turn alter the measured response of the system. Acoustic wave propagation has been extensively used to detect damages in pipelines. Pure technologies using its Soundprint®, an AFO monitoring system, has successfully determined the rate of deterioration in PCCP based on the number of wire breaks during the monitoring period. However, acoustic signals have not been used to assess the foregoing condition of a pipeline. Although the basis for damage detection using acoustic signals appears intuitive, its actual application poses many significant technical challenges. The most fundamental challenge is the fact that damage is typically a local phenomenon and may not significantly influence the global response of a pipe. PCCP PIPE MATERIAL CHARACTERISTICS Figure 1.2: LCP Source: Galleher and Stift 1998. Figure 1.3: ECP Source: Galleher and Stift 1998. PCCP is a composite material of concrete and steel. PCCP is constructed with steel bell and spigot joint rings welded to opposite ends of a steel cylinder which acts primarily as a water barrier. A concrete core and high-strength steel prestressing wire wrapped helically around the core provide the primary structural components. Two types of PCCP have been widely used: lined cylinder pipe (LCP) and embedded cylinder pipe (ECP). In LCP the concrete core is inside the steel cylinder and high-strength steel wire is wrapped around the cylinder. See Figure 1.2. In ECP the steel cylinder is embedded in the concrete core and the prestressing wires are wrapped around the concrete core. A cement-rich mortar coating surrounds the prestressing wires, providing an alkaline environment and protection from external corrosion. See Figure 1.3. LCP has been used for large diameter water transmission and distribution mains since 1942 (AWWA 2007). ECP was developed and first installed in 1953 (Romer et al. 2008). The diameter ranges for LCP and ECP are 16 to 60 inches and 30 to 256 inches, respectively. AWWA standards for design and manufacture of PCCP have primarily been 3 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. governed by AWWA C301 since 1952 and AWWA C304 since 1992 (Villalobos 1998). The initial structural design requirements for the manufacturing of PCCP tended to be conservative (AWWA 1979, Interpace 1973, and ACPA 2007) with high factors of safety. However, as understanding of the behavior of PCCP increased, and advances were made in material sciences, changes in the structural design of PCCP were made to reduce the cost of manufacturing. The increase in the applied tensile strength to the wire during manufacturing in the late 1960s and early 1970s, reduced the amount of prestressing steel wire and allowed wire of smaller diameter, which resulted in what appeared to be a more efficient design and economical manufacturing. After pipe from this era started experiencing a high rate of premature failures the engineering and manufacturing standards for PCCP began to improve. The major revisions in the standards, design, and manufacturing of the PCCP consist of changes in the maximum diameter of the PCCP, the quality and strength of the concrete, the thickness of the steel cylinder, prestressing wire standards, and the thickness of the mortar coating (Price, Lewis, and Erlin 1998). HOW PCCP FAILS All pipes exist in a causal world; that is, cause and effect are deterministic and not random. The fact that PCCP fail structurally after decades of service implies that the applied loads (structural demand) were beyond the design structural capacity or that the structural capacity or demand of the pipe has changed over time. Surge events have been reported as preceding several catastrophic failure of PCCP. Multiple causes for PCCP failure have been reported in the literature: a high chloride environment (Villalobos 1998), poor quality of mortar coating (Price, Lewis, and Erlin 1998), poor quality of prestressing wire (Walsh and Hodge 1998, Knowles 1990), a corrosive environment (Galleher and Stift 1998), inadequate thrust resistance (Ojdrovic et al. 2001), construction damage (Parks, Drager, and Ojdrovic 2001), cracks in the cylinder welds (Price 1990), delamination of coating (Price 1990), and hydrogen embrittlement (Romer et al. 2008). Over time each of these modes results in some combination of electrochemical deterioration of the wire and cylinder, and fatigue of the pipe structure. Hydrogen embrittlement, one of the primary failure modes for PCCP with Class IV wire, decreases both wire ductility and fatigue resistance (Lewis 2002). As each wire in a PCCP breaks, the individual pipe’s strength is incrementally reduced. PCCP failure resulting from steel cylinder corrosion is not typical. The investigator’s experience would say less than 10% of the PCCP failures are due to cylinder corrosion. Generally, steel cylinder corrosion shows up as a failure mechanism when operating pressures are well below design limits and fluctuating groundwater environments are present in the pipe zone. Figure 1.4: Wire breaks Catastrophic PCCP failures are generally due to loss of lead to PCCP failure structural integrity due to accumulation of broken prestressing wires, leading to loss of compression in the concrete core. Once core compression is compromised, structural failure is imminent (Price 1990). Figure 1.4 displays how PCCP failure is precipitated by wire breaks. 4 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. For this reason, all assessment or monitoring methods try to measure wire breaks or assess concrete core compression using various techniques for excitation, measurement of a response and comparison of the excitation or response to accepted norms or calibrations. Wire break counts are then used to evaluate the structural capacity of the pipe based on its original design, material information and data, surge and operating conditions, and any known modifications to design conditions after installation. To avoid failures, reliable wire break data must be combined with appropriately sophisticated structural models to allow a PCCP owner to make timely repair or replace decisions. This PCCP management cycle is described in Figure Figure 1.5: PCCP management cycle 1.5. CONDITION ASSESSMENT OF PCCP Current PCCP assessment methods provide a baseline condition, in the form of wire break quantities or locations of loss of core compression, while monitoring methods capture on-going distress. Commercially available baseline assessment methods include electromagnetic, visual and sounding inspections, which sometimes require dewatering or depressurizing the pipe. Internal Visual Inspection and Aural Sounding Visual inspections look for circumferential and longitudinal cracking. Sounding inspections listen for large hollow areas indicating loss of core compression. Sounding is a subjective acoustic measurement of structural condition. Impact Echo The impact echo (IE) test method and its use in testing concrete pipe have been described in detail in previous publications (Sack and Olson 1994, Sack and Olson 1998, Olson et al. 1992, Sansalone and Carino 1986). The IE method is performed on a point-by-point basis by hitting the test surface at a given location with a small (90 gm [0.2 lb]) instrumented impulse hammer or impactor and recording the reflected wave energy with a displacement or accelerometer receiver mounted to or pressed against the test surface adjacent to the impact location. It provides an indication of thickness measurement for the PCCP core and outer mortar. Reflections from sound areas of the pipe cover a longer path and thus take a longer time to reflect to the receiver. Over an area with an outer mortar delamination, the signals cover a shorter path and thus reflect quicker to the receiver. Since the reflections are more easily identified in the frequency domain, the time domain test data of the impulse hammer (if measured) and receiver are processed by the data acquisition system for frequency domain analyses. Electromagnetic Inspection Electromagnetic inspections estimate the number of broken prestressing wire wraps in a pipe section. Electromagnetic inspection indirectly measures pipe structural condition by 5 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. analyzing the disruption in an induced electromagnetic signal which accompanies broken prestressing wires. ACOUSTIC MONITORING OF PCCP Principals and Foundation Active, on-going distress can be detected with AFO monitoring. There are two methods of installation. One method attaches fasteners along the length of the installed cable. This method is used where especially large turbulence is expected. A second method does not attach the cable at all except where it enters and exits the pipe. This second method can be performed while the pipe is dewatered or in operation, that is, installed without dewatering or even taking the pipe out of service. For this latter method, the provider of AFO service uses a small drogue that tows a cord into the pipe. The drogue is captured some miles downstream and the cord is used to pull in the fiber optic cable (see Figure 1.6). All of this is done through pressure seals at either end while the pipe is pressurized and operating. Figure 1.6: Live deployment of a fiber optic cable The investigator’s experience indicates that the un-mounted systems are quieter. Contrary to expectation, the cable does not move around much except when the flow velocities exceed about 8 ft./second. This is likely due to the drag on the cable produced by the flow keeping the cable tensioned. The total stress on the upstream mount of the cable increases, but the cable is designed to operate even with hundreds of pounds of force. AFO monitoring directly measures loss of core compression by detecting and locating individual wire breaks as they occur. The ideal condition assessment technique would establish baseline condition while also measuring on-going distress, without dewatering the pipeline or otherwise taking it out of service. Methodologies and History of Use Acoustic monitoring of PCCP is not new. Research on acoustic monitoring began in the early 1990s by the United States Bureau of Reclamation (Travers 1994). Early work focused on detecting large acoustic anomalies using sensors placed at some distance from the anomalies, with suitable equipment for relatively short periods of time, typically a few months to one year. 6 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. The application of fiber optic cable as the acoustic sensor has resulted in higher signal fidelity because the fiber optic cable is acoustically sensitive throughout its entire length. Wire breaks cause an excitation of the pipe structure which propagates through both the pipe structure and the water column. The location, amplitude and frequency characteristics of the corresponding acoustic signal can be measured without attenuation or dispersion of acoustic waves propagating through the water column, an issue which can occur with discrete acoustic monitoring systems. AFO monitoring systems were first installed in 2005 which required a pipeline to be Figure 1.7: Wet AFO deployment dewatered for installation. Recent advances in insertion stack AFO deployment technology have made possible the installation of fiber optic cable using parachutes to pull the cable through the pipeline, as depicted in Figure 1.6. Figure 1.7 depicts the AFO cable being deployed into a pipeline through an insertion stack. Each AFO-detected wire break is added to the total wire break estimate provided by electromagnetic inspections to let a PCCP owner know whether the pipe is at the beginning, middle or end of its useful life. An advanced computational model of the pipe based on its original design and any known modifications after installation answers the question, “How Many Wire Breaks is Too Many?” The output of such a structural model is shown in Figure 1.8. Limit states defined by AWWA C304 are plotted to establish the onset of cracking, cylinder and wire yield, and failure. AFO data lets the PCCP owner literally “listen” to the pipe move through these limit states, allowing for an approach to repair and replacement. Figure 1.8: How many wire breaks are too many? 7 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Discrete or Fixed Sensor Deployment Initial system design was based on work done by the United States Department of the Interior, Bureau of Reclamation and included a dual hydrophone station. The original system concept required multiple stations inserted at regular intervals over the length of the pipeline being monitored. These locations required wet tap or access through existing valves. An obvious advantage of this system is that single monitoring stations can be installed fairly easily if there is access to the outside of the pipe at regular intervals. Another advantage is the apparently low cost of isolated stations. Location of wire break events is usually done by comparing the times of arrival of the acoustic wave as it encounters sensors on either side of the break. This requires that at least two sensors be within the detection range of the wire break. The range over which the Bureau was able to detect wire breaks was sometimes thousands of feet. This was an encouraging result as the number of stations per mile required to monitor a section of pipe might be small for large diameter pipe. Disadvantages of these discrete or fixed stations included the difficulty of interconnecting sensors on the surface, protection of several different access points, damage caused by the hot taps, and flow noise caused by the hydrophone position normal to the flow. In addition, stations may not be suitable for smaller diameter pipelines due to attenuation of the acoustic signal over relatively short distance. Higgins and Paulson (2006) have found a correlation between pipe diameter vs. sensor spacing. Small diameter pipe may require sensor spacing so tight (approximately 100 feet on center) that it would be cost prohibitive for the owner to provide the required number of access location to the pipe to facilitate the survey. To overcome this problem, long hydrophone arrays were developed that could overcome this shortcoming for smaller diameter PCCP. Inserted Sensor Array Deployment A hydrophone array consists of a long cable with several discrete hydrophones along its length inserted into active sewer or water PCCP pipeline at an existing valve or wet tap location. The hydrophone array can be manufactured in various lengths depending on the project requirements. Sensor arrays installed have ranged in length from 1500 feet to over 6000 feet from one insertion point. Once in place, the hydrophones continuously monitor the pipe for acoustic events that exhibit properties characteristic of prestessing wire failures. Because the sensor are submerged directly in the flow, there is an improvement in sensitivity and fidelity in the measurements. Once an event is observed the data are processed by a data acquisition system and compared to preset acoustic criteria. If the acoustic event recorded meets the established criteria, the event is uploaded to a remote site for further evaluation by a trained technician, using proprietary processing software. When an event has been determined to have all the acoustic characteristics of a prestessing wire failure, the analytical software further evaluates the signal to allow for accurate location of the event origin. The speed of sound in water is known as well as the spacing between the hydrophones. By comparing the arrival time between two adjacent hydrophones, the signal processor is able to accurately determine the location of the wire break. Advantages of the hydrophone array over the single station are many. They include: 8 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. 1. 2. 3. An Inserted array requires only one insertion point for up to 6000 feet of pipeline. Inserted Arrays could be manufactured in various lengths to facilitate specific project requirements. The location and spacing of the hydrophones on the Inserted Array can be customized to provide adequate acoustic coverage in various pipe sizes. Acoustic Fiber Optic Monitoring Acoustic monitoring of PCCP uses the energy emitted by breaking prestressing wires to physically locate the site of deterioration or damage. When a prestressing wire breaks or even slips, the energy released due to the break enters the incompressible fluid and propagates along the pipeline and in the pipe wall. Similar to “active sonar”, the energy release constitutes an excitation signal to the pipe structural system. The function response (both pure time domain, frequency domain, along with other transformations) is directly related to the structural integrity of the carrier pipe. By performing detailed analysis of data collected (response functions) from discrete and continuous acoustic monitoring arrays, the structural condition of pipe section on which the break occurs and those in the immediate vicinity can be determined. Pure Technologies currently provides AFO monitoring to more than 147 miles of PCCP in the United States, Canada and Mexico, and more than 340 miles in Libya. Pure Technologies possesses the only known database of spontaneous wire breaks in operating pipelines as detected with distributed fiber optic sensors. Some of the pipes monitored with fiber optic sensors over past years have been excavated and inspected, affording information about the condition of pipes in which spontaneous wire breaks were detected. Importantly, this allows comparison of the results in the field with the output of models and algorithms developed from the controlled, buried test described above. The feedback loop created in this way will improve the practical applicability of results from this work, and test the application to different pipe types and conditions. PROBLEM STATEMENT: PASSIVE CONDITION ASSESSMENT OF PCCP BY PROCESSING ACOUSTIC DATA TO MINE INFORMATION CONDITION ASSESSMENT INFORMATION FROM CONDITION MONITORING SIGNALS The work by Bell et al. (2009) and Bell and Paulson (2010) showed that some aspects of condition can be understood by “data mining” for acoustic events. Data mining is a branch of computer science is the process of extracting patterns from large data sets by combining methods from statistics, transformations and, possibly, artificial intelligence and database management. Data mining is seen as an increasingly important tool by modern business to transform data into actionable information. Data mining is currently used in a wide range of profiling practices, such as marketing, surveillance, fraud detection, and scientific analysis. The manual extraction of patterns from data has occurred for centuries. Early methods of identifying patterns in data include Bayes' theorem (1700s) and regression analysis (1800s). The proliferation, ubiquity and increasing power of computer technology has increased data collection, storage and manipulations. As data sets have grown in size and complexity, direct hands-on data analysis has increasingly been augmented with indirect, automatic data processing. This has been aided by other discoveries in computer science, such as neural networks, clustering, genetic algorithms (1950s), decision trees (1960s), and support vector machines (1980s). Data mining is 9 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. the process of applying these methods to data with the intention of uncovering hidden patterns. It has been used for many years by businesses, scientists and governments to sift through volumes of data such as airline passenger trip records, census data and supermarket scanner data to produce market research reports. A primary reason for using data mining is to assist in the analysis of collections of observations of behavior. Such data are vulnerable to co-linearity because of unknown interrelations. An unavoidable fact of data mining is that the set(s) or subset(s) of data being analyzed may not be representative of the whole domain, and therefore may not contain examples of certain critical relationships and behaviors that exist across other parts of the domain. To address this sort of issue, the analysis may be augmented using experiment-based and other approaches, such as Choice Modeling for human-generated data. In these situations, inherent correlations can be either controlled for, or removed altogether, during the construction of the experimental design. Data mining commonly involves four classes of tasks: Clustering – is the task of discovering groups and structures in the data that are in some way or another "similar", without using known structures in the data. Classification – is the task of generalizing known structure to apply to new data. For example, an email program might attempt to classify an email as legitimate or spam. Common algorithms include decision tree learning, nearest neighbor, naive Bayesian classification, neural networks, and support vector machines. Regression – attempts to find a function which models the data with the least error. Association rule learning – searches for relationships between variables. For example, a supermarket might gather data on customer purchasing habits. Using association rule learning, the supermarket can determine which products are frequently bought together and use this information for marketing purposes. This is sometimes referred to as market basket analysis. The final step of knowledge discovery from data is to verify the patterns produced by the data mining algorithms occur in the wider data set. Not all patterns found by the data mining algorithms are necessarily valid. It is common for the data mining algorithms to find patterns in the training set which are not present in the general data set, a phenomenon called “over-fitting.” To overcome this, the evaluation uses a test set of data that the data mining algorithm was not trained on. The learnt patterns are applied to this test set and the resulting output is compared to the desired output. For example, a data mining algorithm trying to distinguish spam from legitimate emails would be trained on a training set of sample emails. Once trained, the learnt patterns would be applied to the test set of emails on which it had not been trained. The accuracy of these patterns can then be measured from how many emails they correctly classify. A number of statistical methods may be used to evaluate the algorithm, such as receiver operating characteristic (ROC) curves. If the learnt patterns do not meet the desired standards, then it is necessary to reevaluate and change the preprocessing and data mining. If the learnt patterns do meet the desired standards then the final step is to interpret the learnt patterns and turn them into knowledge. The process of “data mining” from data intensive streams is not unique to acoustic events in PCCP and the Principal Co-Investigators are familiar with the processes. Reid, Bell and Edgemon (1998) used simple statistical “data mining” processing (skew and kurtosis) of electrochemical signals to characterize and identify types of localized corrosion (stress corrosion 10 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. cracking, pitting, etc.) and, eventually, train neural networks for real time and post processing. Mr. Paulson (unpublished) used similar methods in discriminating acoustic wire break signals in unbonded post-tensioning cables from normal noise resulting from construction and other activity in a structure using artificial learning networks. Dr. Alavinasab (Tehranizadeh et al. 2003) used similar methods to develop a competitive (unsupervised) learning neural network algorithm for extruding the key characters of thousands of measured earthquake signals according to their corresponding soil types. No matter the system being “mined” the processes are the same. EXTENSION OF PCCP CONCEPTS TO PIPE WALL ASSESSMENT FOR OTHER PIPE MATERIALS Acoustic data collection and analysis has been used to assess the condition of non-PCCP using both fixed (inside or outside the pipe) and moving (inside the pipe) sensors. The propagation of low frequency acoustic waves through fluid-filled pipes is affected by the characteristics of the wall of the pipe (Long, Cawley, and Lowe 2003; Hunaidi 2006). The process of using propagation velocity to assess pipe wall condition is known as acoustic pipe wall assessment (PWA). PWA using a moving receiver within the pipeline is inherently far more detailed and precise than the use of fixed sensors at large separation distances. Using a moving sensor or sensors can reveal spatial distribution of anomalies, gradients, amplitudes and manufacturing variances in the pipe wall. An example of a PWA result collected in a metallic pipeline using a moving sensor (Pure Technologies’ SmartBall®) is shown in Figure 1.9. Depending on the pipe size and flow condition, the technology is currently able to access the pipe wall condition at intervals of approximately 3 inches. As shown in Figure 1.9, the data reveals the joints in the line in addition to three anomalies for a section approximately 165 feet in length. Figure 1.9: Example of PWA using a moving sensor This technology does not measure the pipe wall thickness, but instead measures the pipe wall hoop stiffness; more specifically the variance in the pipe wall hoop stiffness. The rationale for this has resulted from observations which indicate burial conditions and natural variances of pipe wall thickness from the manufacturer are never well known. However, because neither of these conditions changes over short spatial distances, data representing the relative apparent stiffness can yield useful data about the structural integrity of the pipeline. 11 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Known limitations in measuring propagation velocity of an acoustic wave currently apply to PWA. These issues result from the need to measure very small changes in arrival times of waves that exhibit very slow slew rates due to their low frequency. Typical frequencies used are a few hundred Hertz or less, while resolution of 20–30 microseconds is desired to accurately measure the variations in local hoop stiffness of the pipes through which a sensor is moving. 12 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. CHAPTER 2: LITERATURE SURVEY ON RESEARCH TOPICS BACKGROUND ON ACOUSTICS, SOUNDS AND SIGNALS Acoustic signals associated with wire breaks have been used to assess PCCP integrity for more than 20 years. The focus of this research is to characterize the sounds and signals which result from the energy release from wire breaks events (Bell et al. 2009). Acoustic signals, sounds of wire breaks, in solids (PCCP pipe walls) are comprised of both compression and shear waves. Only compressive waves exist in fluids, because they cannot sustain shear stress. Compressive waves are related to compressibility and density of the fluid or solid. Shear waves only occur in solids and are related to material stiffness, compressibility and density (Rossing et al. 2003). For PCCP, compressibility and density of the material does not change, but apparent stiffness changes as wires break, prestress in the concrete core is lost and delamination of exterior mortar occurs. Analysis of measured acoustic signals from PCCP wire breaks basically comes down to processing the digital signals so that identifying, characterizing and discriminating between these signals is possible. Understanding and characterizing sounds is an integral part of this research. Sounds may generally be characterized by pitch (frequency), loudness (amplitude) and quality or timbre. Timbre allows one to distinguish between sounds with the same pitch and loudness. Timbre is mainly determined by the harmonic (mix of frequencies) and dynamic (changes in amplitude and frequency) characteristics of the sound (Rossing et al. 2003). The primary contributors to timbre or quality are harmonic content, vibrato, attack and decay (Rossing et al. 2003). Harmonic content is the number and relative intensity of upper harmonics in the sound and associated overtones. Harmonics and overtones can be analyzed and characterized by transformations from the time domain to the frequency domain (Rossing et al. 2003). This was the focus of Bell et al. (2009). The ordinary definition of vibrato is "periodic changes in the pitch of the tone," and the term tremolo is used to indicate periodic changes in the amplitude or loudness of the tone. So vibrato could be called FM (frequency modulation) and tremolo could be called AM (amplitude modulation) of the tone. Actually, in the voice or the sound of a musical instrument both are usually present to some extent. Because the acoustic events from wire breaks on PCCP are discreet and not sustained, vibrato is not considered an important characteristic of these acoustic events (Rossing et al. 2003). Figure 2.1 shows the attack and decay of a plucked guitar string. The plucking action gives it a sudden attack characterized by a rapid rise to its peak amplitude. The decay is long and gradual by comparison. The ear is sensitive to these attack and decay rates and may be able to use them to identify the instrument producing the sound (Rossing et al. 2003). 13 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 2.1: Pluck of a guitar string showing characteristic attack and decay Figure 2.2 shows the sound envelope of striking a cymbal with a stick. The attack is almost instantaneous, but the decay envelope is very long. The time period shown is about half a second. The interval shown with the guitar string above is also about half a second, but since its frequency is much lower, you can resolve the individual periods in that sound envelope. Because of the high frequencies in the cymbal strike, the individual periods cannot be discerned within the acoustic signal. This type of signal is most similar in shape to PCCP wire breaks as depicted in Figure 2.3 (Rossing et al. 2003). Figure 2.2: Striking of a cymbal showing characteristic attack and decay. 14 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. The concepts of timbre, pitch and loudness could be useful in the analysis data since they are similar to the processing that the human brain conducts when analyzing sounds. ACOUSTIC, EMISSION, MONITORING AND SOUNDS OF PCCP The use of acoustic monitoring of PCCP is not new (Worthington 1998, Paulson 1998a, Paulson 1998b). Research on acoustic monitoring began in early 1990’s by the Bureau of Reclamation (Travers 1994, Worthington 1992). Results up to this point have focused on “listening” for large distinctive acoustic anomalies or events using sensors placed at some distance from the anomalies, with suitable equipment for relatively short periods of time, typically a few months to one year (Holley and Buchanan 1998). When wire break activity was detected, in most cases, only a few acoustic events were recorded due to the limited installation time. Nonetheless, valuable information was obtained from these installations (Higgins 2004). The advent of fiber-optic cable (FOC) as an acoustic sensing element for acoustic monitoring of PCCP results in higher signal fidelity because FOC is acoustically active along its entire length (Higgins and Paulson 2006, Essamin and Holley 2004, Lenghi et al. 2008). A typical acoustic event is shown in Figure 2.3. The location, amplitude and frequency characteristics of the acoustic events (AE) and the acoustic response of the structure transmitted through the water column are recorded without the attenuation which can occur with discrete acoustic sensing systems. These improvements in technology have lead to longer monitoring times and the recording of literally thousands of wire break acoustic events with very high fidelity from pipes with a wide variety of conditions (Bell and Paulson 2010). Figure 2.3: Typical wire break Source: Bell and Paulson 2010 The collection of acoustic monitoring signals and their relation to pipe condition has always been an issue. In its simplest form, acoustic signals count wires that break while you are listening, but cannot tell you how many wires were broken before you started listening. In short, acoustic monitoring can give you a rate of wire breaks, but not the integrated amount of broken wires. In addition, the location of wire breaks can be estimated to within about one pipe diameter using acoustic triangulation from hydrophones or fiber optic cable installation and the time of wire breaks and time between wire breaks can be very accurately recorded. This level of information 15 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. allows correlation of wire break events with operational or external changes and permits causation to be investigated. However, as discussed above, the condition (structural integrity and serviceability of the pipe) are related to the integrity/condition and number of intact prestressing wires. Wrigglesworth and Higgins (2010) found that by monitoring the rate and change in rate of wire breaks using acoustic monitoring, catastrophic failures could be avoided. Stroebele et al. (2010) found that depressurization and repressurization of PCCP for shut down produced wire break acoustic events. The ability of acoustic emission and monitoring to distinguish between wire breaks, wire slips, mortar delaminations and concrete core cracking which also occur as the pipe condition deteriorates was uncertain from the beginning. Bell and Paulson (2010) used empty, dry above grade lined cylinder PCCP to collect data on lined cylinder pipe and recorded acoustic equivalent data associated with prestressing wire being cut and with relaxation (wire slips, mortar delaminations and concrete core cracking) over time. They concluded that wire breaks were distinguishable from wire slips, mortar delaminations and concrete core cracking based on amplitude. The amount of energy released from the breaking of a prestressing wire is many orders of magnitude greater than that associated with wire slips, mortar delaminations and concrete core cracking. This makes sense because the tensile strength of the wires is at least three orders of magnitude greater that tensile strength of concrete and interfacial shear strength of smooth steel on concrete. In short, wire breaks are unique, identifiable and distinguishable based on acoustic characteristic (pitch and loudness or amplitude) from other deterioration events for PCCP (Bell and Paulson 2010). CURRENT STATE OF CONDITION ASSESSMENT FOR PCCP Current PCCP assessment methods provide a baseline condition, in the form of wire break quantities or locations of loss of core compression, while monitoring methods capture on-going distress. Commercially available baseline assessment methods include electromagnetic, visual and sounding inspections, which sometimes require dewatering or depressurizing the pipe. Electromagnetic inspections estimate the number of broken prestressing wire wraps in a pipe section, while visual and sounding inspections look and listen for circumferential cracking and large hollow areas indicating loss of core compression (Gallaher and Stift 1998). Electromagnetic inspection indirectly measures pipe structural condition by analyzing the disruption in an induced electromagnetic signal which accompanies broken prestressing wires, while sounding is a subjective acoustic measurement of structural condition. Active, on-going distress can be detected with AFO monitoring which can typically be installed without dewatering or even taking the pipe out of service. AFO monitoring directly measures loss of core compression by detecting and locating individual wire breaks as they occur. The ideal condition assessment technique would establish baseline condition while also measuring on-going distress, without dewatering the pipeline or otherwise taking it out of service. In contrast to acoustic monitoring, electromagnetic inspections estimate the accumulated damage at any point in time on pipe segment. Periodic electromagnetic inspections could provide estimates of the number of broken wires and approximate location on a pipe segment, but the rate of wire breaks could only be inferred by consecutive electromagnetic inspections and causation cannot be inferred. Whether the technology is electromagnetic (Mergelas and Kong 2001) or physical (Gallaher and Stift 1998) or a combination of techniques (Fitamant et al. 2004), condition assessment for PCCP fundamentally comes down to correlating changes in an excitation signal 16 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. and a measured response signal. For electromagnetic condition assessment, changes in amplitude and phase of essentially radio signals infer prestressing wire continuity and thereby indirectly the structural condition of the pipe (Fitamant et al. 2004). For physical sounding, the changes in sound measured using the human ear by physical excitation by striking the internal wall of the pipe infer the condition of the pipe wall. The relationship and characteristics of the response are compared with the excitation. The signal changes can then be correlated with the condition or changes in the condition of the system. CURRENT STATE OF ACOUSTIC SIGNAL PROCESSING AS APPLIED TO PCCP This research focuses on using the energy released by the wire break as the acoustic excitation signal and measure acoustic signals to assess the condition of the pipe wall. Bell and Paulson (2010) showed that some aspects of condition can be understood by data mining. Bell et al. (2009) and Bell and Paulson (2010) looked at simple frequency domain transformations and statistical methods of “characterizing” the data and looking for trends. The previous work suffered from two distinct limitations. Bell et al. could not verify or correlate the changes in mathematical results with actual changes in structural condition and changes were not traceable to unique pipes. Other methods of data processing or, more likely, combinations of methods may give more insight into the condition assessment. Bell and Paulson (2010) indicates it may be possible to harvest condition information from acoustic data. In this work, acoustic emission data was collected and analyzed for a 72-inch San Diego County Water Authority PCCP pipeline which failed catastrophically while being monitored with AFO. The acoustic data analyzed in the time domain and other transformed domains as the intervals between wire breaks decreased and the pipe ruptured. Initially, the time between wire breaks was days, then hours, then minutes. The work supported the conclusion that redistribution and increases in local stresses occur as wires break and other wires in the vicinity carry the additional load. As the stresses increase locally, wires break more frequently and the pipe “unzips” with the time between wire break acoustic events decreasing as the system (pipe) becomes less restrained and more unstable. Bell et al. (2009) also examined time domain plots, transformed to the power spectral density (PSD) frequency domain using Fourier Transforms and integrated, for two specific normalized acoustic events associated with wire breaks: one just minutes before failure (Figure 2.5) and one several days before failure (Figure 2.4). The differing PSD frequency characteristics led Bell et al. (2009) to the conclusion that the dominant frequencies for wire breaks could be related to the overall pipe condition. 17 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 2.4: Integrated power spectral density of first normalized acoustic event days prior to failure Source: Bell et al. 2009 Figure 2.5: Integrated PSD of normalized sub-event in acoustic event less than an hour before failure Source: Bell et al. 2009 Subsequent work (Bell and Paulson 2010) studied wire breaks, wire slips and delaminations in PCCP. Above-grade 42-inch sections of PCCP were instrumented and wires systematically cut while acoustic and mechanical distortion data were collected (Figure 2.6). Instantaneous changes along with relatively long-term relaxation of the pipe were monitored. Acoustic signals were correlated to mechanical measurements and observations of wire breaks, wire slips and delaminations of the mortar coating. 18 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Bell and Paulson (2010) clearly demonstrated how the delamination from a wire break affected the signal from an adjacent wire break. A wire break adjacent to an area where delamination has occurred would have a larger redevelopment length than would otherwise have been the case. In that case, the total energy released by the new wire break will typically be larger and the energy spectrum will shift downwards in frequency. As the delaminated area enlarges with additional wire breaks, the total energy released by each wire break will increase by an order or more. For multiple wire breaks in an area, Bell and Paulson (2010) also demonstrated the signal process distinction between a wire break and the “relaxation” of a wire that has already broken. There is virtually no acoustic energy produced by relaxation of the wire after it has broken. This has been confirmed by empirical studies by the investigators completed over protracted periods of time. Delaminations are sometimes detected but differ greatly in their acoustic character from wire breaks and the distinction is easy to make. Acoustic signal processing can distinguish multiple wire breaks within a short time span in a given pipe area. The investigator’s experience (Bell and Paulson 2012) indicates that even in instances where one wire break (apparently) causes adjacent wires to break, the acoustic signals do reveal the number of wires that fail, even when the occurrence is within a few milliseconds. The sampling rate of typical equipment is such that in order for events to be “simultaneous” they would have to occur within 15 microseconds of each other. The spatial resolution of the signals is such that events would have to be within one meter of each other. Given the causal rather than random nature of wire breaks, the probability of apparently simultaneous while spatially similar events occurring is small. The only case when this might occur would be during a catastrophic failure (short time scale, large length scale). Bell and Paulson (2010) concluded that wire breaks were associated with large amplitude in the time domain and relatively flat frequency distribution, whereas delaminations were associated with lower amplitude and dominant frequencies less than 2 kilohertz (kHz). The difference between the reported dominant frequencies in 72-inch PCCP under operational pressure and 42-inch PCCP without internal pressure indicates that the acoustic energy release from a wire break event could be a function of pipe type, diameter, thickness, and class of prestressing wires, and internal and external loads on the Figure 2.6: Aboveground PCCP instrumented pipe. with strain gages and displacement monitoring The work by Bell et al. (2009) and physical scales Bell and Paulson (2010) showed that some aspects of condition can be understood by “data mining” for acoustic events. The process has been shown to be feasible, but more work needs to be done to make the observation useful. In addition, Bell et al. (2009) and Bell and Paulson (2010) looked at simple frequency domain transformations and statistical methods of “characterizing” the data and looking for trends which may be related to the structural condition of PCCP (e.g. broken prestressing wires, loss of concrete compression or mortar delaminations). 19 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Other methods of data processing or, more likely, combinations of methods will give more insight into the condition availability to the project of the unpublished details of the prior research, including the investigators’ insight into improvements into testing apparatus, acoustic analytical methods, and unpublished assessments that failed to produce results. OTHER CANDIDATE TECHNIQUES FOR PROCESSING ACOUSTIC SIGNALS FROM PCCP WIRE BREAKS The literature of signal processing is very mature and robust compared to the techniques originally applied by Bell and Paulson (2010). Signal processing is focused in the electrical engineering field and many of them for condition monitoring of rotating and other mechanical equipment (Grimmelius et al. 1999). From a fundamentals standpoint, there are three different condition monitoring techniques: first principles, feature extraction, and neural networks (Grimmelius et al. 1999). Acoustic signals can be processed in much the same way (Rossing et al. 2003). A first principles method uses mathematical simulation models based on first principal physics to predict the behavior of machinery, both for healthy and faulty conditions. One of the main characteristics of these simulation models is the required high level of knowledge of those processes. They require extensive knowledge of the “first principles,” such as conservation laws, and of constitutional laws, such as the properties of matter. Measured data is required for tuning, validation, and verification (Grimmelius et al. 1999). The first principles approach is probably not the most viable method for PCCP wire break analysis at this time, due to the non-uniformity of the manufacturing process, the heterogeneity of the PCCP composite structure and complexity of the applied loads. Feature extraction and pattern recognition algorithms are used for analyzing signals and for classifying (parts of the) signals into classes. The classification is done by matching (part of) the signal with a set of reference signals. The sensor signal will be classified as a member of the class that corresponds with the best matching reference signal. The isolation of parts of the signal those are unique for the classes’ results in a better control of the classification problem. In this way, the influence of fluctuations in the sensor signal which are caused by instabilities and noise will be reduced to a minimum (Grimmelius et al. 1999). The process of isolating those parts of the sensor signal is called the feature extraction process, while the matching process is known as pattern recognition. This is the first step in analysis, particularly when limited data with known excitation/response information is available and will be the at least the initial focus of the efforts on the project. Neural network technology is used to recognize and classify complex fault patterns without much knowledge about the process, the signals, or the fault patterns themselves. A neural network consists of many simple neurons which are connected with each other. The behavior of the network is determined by the (adjustable) weights that are associated with each connection. The values of these weights are determined during the training session. During this session, examples of the different situations (input patterns with corresponding output classifications) are presented to the neural network. Neural networks tend to be very robust to noise in the signals (Sarle 1998). Application of neural network technology requires a large training data set, covering all classes of conditions that are required to be detected. The results of a neural network are only valid within the range of this training data set. Reid et al. (1998) trained neural networks to identify electrochemical noise signals from localized and uniform corrosion phenomenon. For this application, a large number of well characterized data sets were available to train the network 20 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. before using the neural network to analyze real time datasets. On the other hand, the ability of neural networks to “train” themselves sometimes allows neural networks to find a solution where other methods fail (Grimmelius et al. 1999). Once a better understanding of signals and system responses are developed, neural networks may ultimately be utilized, but for this research, since insufficient quality excitation/response data exists to train the a neural network, neural networks will have to be the a future objective. TIME DOMAIN PATTERN OR CHARACTERISTIC ANALYSIS Power and Energy (Amplitude) Signal Information The energy of an acoustic signal is proportional to the square of the amplitude of the signal. When a wire breaks the energy release is related to the ‘stress state’ which exists in the wire at the location of the break. Since wire breaks result in changes in the local stress state of the pipe, analysis of amplitude and energy is related to the stress state and ultimately the condition of the pipe at the location where the wire breaks. Energy analysis, spectral and otherwise, is most applicable to systems that have finite total energy (e.g. pulse like signals such as what occurs when a wire breaks). Amplitude and energy have been used by analysts in many forms to discriminate and validate acoustic signals from PCCP pipe. Bell and Paulson (2010) were able to show that energy/amplitude could be used to discriminate between wire breaks and mortar cracking/delamination events. Power (i.e. energy per unit time) characterization of acoustic signals has been applied in many systems and is similar to energy characterization; power characterization is most appropriate for stationary processes. For continuous signals that describe stationary physical processes, it makes more sense to define a power spectral density (PSD), which describes how the power of a signal or time series is distributed over the different frequencies. The above definition of energy spectral density is most suitable for transients; that is, pulse-like signals, for which the Fourier transforms of the signals exist, is most suitable for the purposes investigated here. Time Between Wire Breaks (Wire Reliability) Although not investigated in this work, wire reliability is worth discussion. Reliability theory is a scientific approach aimed to gain theoretical insights into mechanisms of survival patterns by applying a general theory of systems failure. Basically, if we assume that each wire is part of a population of wires which will eventually fail (failure = unable to perform its intended function), that the wires in the population were manufactured with the same processes and flaws and the wire in the population are subjected to the same environment (on average), then we can use reliability theory to predict the trend in wire breaks. This is very similar to the process that Romer et al. (2008) developed for PCCP pipe failures and others have applied to various pipe break models such as KANEW. The process would be similar. Advantages of the technique are that it does not require any mechanistic information about the processes and works simply from wire break data from the actual system, so it is internally self-consistent and deterministic. The disadvantages are that in order to be statistically significant, dozens of wire breaks are needed to establish models, the assumption that the influencing factors are stationary and the inability of the reliability function to determine the structural condition of a pipe or which specific pipe segment is at risk. Wire reliability modeling may be useful in some specific large populations of PCCP 21 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. where large numbers of wire breaks can be tolerated and used to analyze all wire breaks and pipe designs and operating characteristics are sufficiently similar such that the stationary assumption is valid, but it was not investigated in this work. FEATURE EXTRACTION AND ANALYSIS METHODS Fourier Transforms Fourier's representation of functions as a superposition of sine and cosine function has become ubiquitous for both the analytic and numerical solution of differential equations and for the analysis and treatment of communication signals. The Fourier transform's utility lies in its ability to analyze a signal in the time domain for its frequency content. The transform works by first translating a function in the time domain into a function in the frequency domain. The signal can then be analyzed for its frequency content because the Fourier coefficients of the transformed function represent the contribution of each sine and cosine function at each frequency. An inverse Fourier transform transforms data from the frequency domain into the time domain (Lathi 2000). Discrete Fourier Transforms The discrete Fourier transform (DFT) estimates the Fourier transform of a function from a finite number of its sampled points. The sampled points are supposed to be typical of what the signal looks like at all other times. This was the methodology of Bell and Paulson (2010). The DFT has symmetry properties almost exactly the same as the continuous Fourier transform. In addition, the formula for the inverse discrete Fourier transform is easily calculated using the one for the discrete Fourier transform because the two formulas are almost identical (Lathi 2000). Windowed Fourier Transforms If f(t) is a nonperiodic signal, the summation of the periodic functions, sine and cosine, does not accurately represent the signal. You could artificially extend the signal to make it periodic but it would require additional continuity at the endpoints. The windowed Fourier transform (WFT) is one solution to the problem of better representing the nonperiodic signal. The WFT can be used to give information about signals simultaneously in the time domain and in the frequency domain (Lathi 2000). With the WFT, the input signal data are chopped up into sections, and each section is analyzed for its frequency content separately. If the signal has sharp transitions (Figure 2.3), WFT splits the input data so that the sections converge to zero at the endpoints. This windowing is accomplished via a weight function that places less emphasis near the interval's endpoints than in the middle. The effect of the window is to localize the signal in time (Lathi 2000). Fast Fourier Transforms To approximate a function by samples, and to approximate the Fourier integral by the discrete Fourier transform, requires applying a matrix whose order is the number sample points n. Since multiplying an n x n matrix by a vector costs on the order of n3 arithmetic operations, the problem gets quickly worse as the number of sample points increases. However, if the samples are 22 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. uniformly spaced, then the Fourier matrix can be factored into a product of just a few sparse matrices, and the resulting factors can be applied to a vector in a total of order nlog2n arithmetic operations. This is the so-called fast Fourier transform (FFT). Wavelet Transforms Wavelets are mathematical functions that cut up data into different frequency components, and then study each component with a resolution matched to its own scale. They have advantages over traditional Fourier methods in analyzing physical situations where the signal contains discontinuities and sharp spikes (Figure 2.3). Wavelets were developed independently in the fields of mathematics, quantum physics, electrical engineering, and seismic geology. Interchanges between these fields during the last ten years have led to many new wavelet applications such as image compression, turbulence, human vision, radar, and earthquake prediction. The FFT and the discrete wavelet transform (DWT) are both linear operations that generate a data structure that contains log2n segments of various lengths, usually filling and transforming it into a different data vector of length 2n. The mathematical properties of the matrices involved in the transforms are similar as well. The inverse transform matrix for both the FFT and the DWT is the transpose of the original. As a result, both transforms can be viewed as a rotation in function space to a different domain. For the FFT, this new domain contains basis functions that are sines and cosines. For the wavelet transform, this new domain contains more complicated basis functions called wavelets, mother wavelets, or analyzing wavelets (Mallat 2009). Both transforms have another similarity. The basis functions are localized in frequency, making mathematical tools such as power spectra (how much power is contained in a frequency interval) and scalegrams useful at picking out frequencies and calculating power distributions. Dissimilarities between Fourier and Wavelet Transforms The most interesting dissimilarity between these two kinds of transforms is that individual wavelet functions are localized in space. Fourier sine and cosine functions are not. This localization feature, along with wavelets' localization of frequency, makes many functions and operators using wavelets "sparse" when transformed into the wavelet domain. This sparseness, in turn, results in a number of useful applications such as data compression, detecting features in images, and removing noise from time series. One way to see the time-frequency resolution differences between the Fourier transform and the wavelet transform is to look at the basis function coverage of the time-frequency plane. Figure 2.7 shows a windowed Fourier transform, where the window is simply a square wave. The square wave window truncates the sine or cosine function to fit a window of a particular width. Because a single window is used for all frequencies in the WFT, the resolution of the analysis is the same at all locations in the time-frequency plane. 23 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 2.7: Fourier basis functions, time-frequency tiles, and coverage of the timefrequency plane. Source: based on Graps 1995 An advantage of wavelet transforms is that the windows vary. In order to isolate signal discontinuities, one would like to have some very short basis functions. At the same time, in order to obtain detailed frequency analysis, one would like to have some very long basis functions. A way to achieve this is to have short high-frequency basis functions and long low-frequency ones. This happy medium is exactly what you get with wavelet transforms. Figure 2.8 shows the coverage in the time-frequency plane with one wavelet function, the Daubechies wavelet. Figure 2.8: Daubechies wavelet basis functions, time-frequency tiles, and coverage of the time-frequency plane. Source: based on Graps 1995. One thing to remember is that wavelet transforms do not have a single set of basis functions like the Fourier transform, which utilizes just the sine and cosine functions. Instead, wavelet transforms have an infinite set of possible basis functions. Thus, wavelet analysis provides immediate access to information that can be obscured by other time-frequency methods such as Fourier analysis. Monte Carlo Techniques for Signal Processing In general, Monte Carlo methods are used in mathematics to solve various problems by generating suitable random numbers and observing that fraction of the numbers which obeys some property or properties. The method is useful for obtaining numerical solutions to problems which 24 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. are too complicated to solve analytically. The most common application of the Monte Carlo method is Monte Carlo integration. A large number of statistical signal processing applications including filtering, estimation, and detection require evaluation of integrals, optimization and simulation of stochastic systems. These methods have not only played a prominent role in the field of signal processing but also in physics, econometrics, statistics, and computer science. In many problems encountered in signal processing, it is possible to accurately describe the underlying statistical model using probability distributions. Statistical inference can then theoretically be performed based on the relevant likelihood function or posterior distribution in a Bayesian framework. However, most problems encountered in applied research require non-Gaussian and/or nonlinear models to correctly account for the observed data. In these cases, it is typically impossible to obtain the required statistical estimates of interest [e.g., maximum likelihood (ML) or conditional expectation] in closed form as it requires integration and/or maximization of complex multidimensional functions. This is where Monte Carlo methods are valuable. PIPE WALL ASSESSMENT FOR OTHER PIPE MATERIALS All condition assessment methods rely on an excitation signal and measurement of a response of the pipe system to the applied response. Most pipe wall assessment (PWA) methods have focused on electrical or magnetic properties for excitation and response. For PCCP, remote field eddy current transformer coupling has been successfully applied as a wire and pipe wall condition assessment methodology using different insertion platforms (Mergelas and Atherton 1998, Mergelas and Kong 2001, Romer et al. 2008). For steel and iron pipe, magnetic flux leakage has been applied to measure wall loss and damage (Hannaford et al. 2010). An overview of methods is given by Prinsloo, Wrigglesworth and Webb (2011). Acoustic methods for PWA have not received as much attention. Due to its composite nature, PCCP has an intrinsic energy source for condition assessment excitation, the prestressing wires. In the case of PCCP and this work, we use the unfortunate or uncontrolled energy release of a wire break as the excitation signal and measure and analyze the acoustic response of the structural pipe wall system. Other pipe materials such as steel, ductile iron, PVC and HDPE do not have similar “intrinsic” excitation sources. Since these monolithic pipe materials do not have an excitation source, one must be provided along with a sensor for measuring the response. The concept for this project is to use tethered exciters with response sensors to in-situ measure the change in radial stiffness as a function of axial position. We were unable to find any similar work in the literature. SUMMARY OF THE LITERATURE While the literature for signal processing analysis is extensive, the work on processing and analyzing signals from PCCP wire breaks has been limited. Amplitude analysis and statistics are promising because they have been used intuitively by analyst to identify wire breaks, but codification of the processes has been limited. Advanced mathematical methods have application, but how robust these techniques are for field application is yet to be seen. The proof will be in the analysis of both experimental and real data and understanding which methods translate under which conditions. 25 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. ©2014 Water Research Foundation. ALL RIGHTS RESERVED. CHAPTER 3: EXPERIMENTAL SET-UPS, TESTING PROCEDURES, AND DATA MINING REPOSITORY PASSIVE CONDITION ASSESSMENT OF PCCP FACILITY Design of the Facility of PCA-PCCP Facility The test set-up concept was conceived and designed by the investigators. Figure 3.1 depicts the engineering drawings of the test set-up. The design took into account several significant variables that were anticipated. These included: Frozen ground – Frozen ground was anticipated to be near the pipe, but not in contact with the pipe as the water will always transfer heat to the surrounding. This was predicted to be the exact case when the first cuts were planned to be performed in the experiment. As the ground thaws continually further from the pipe wall, replicate cuts were planned to be used to ascertain the effect of the increasing distance to frost line. The hope was that the regression of frost would be slow enough to be tracked while the cuts were made. Pipe size – Pipe size was not a variable that could be tested with the designed configuration. However, much data from different pipe sizes and configurations is already available and can be analyzed in the future for sensitivity to pipe size. Water pressure – Water pressure was expected to have an effect on the spectral content, but not to the degree expected as the compression level changes. At least two different pressures were planned to be used during the tests to establish the sensitivity of the response to water pressure. Water flow – Water flow was not expected to contribute significantly to local spectral content. The designed test setup could not provide flow. However, data from real world monitoring of pipes can be mined to establish if there is an obvious sensitivity of spectral content to flow rates. 27 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 3.1: Engineering drawing of test set-up 28 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. The City of Calgary’s pipe yard served as the test site for the pipe burial. In-kind support from the City included the allocation and clean-up of a parcel of land for pipe burial. Figure 3.2 shows a site map of the burial setup, located at 14444 Bearspaw Dam Rd. NW, Calgary, AB. Figure 3.2: Pipe burial site map The burial of the pipe test set-up had to be performed before the start of winter. Any additional delay would have pushed testing and data collection work to late-spring, which could have resulted in a loss of the City of Calgary’s budgeted in-kind support. Three (3) 42-inch PCCP-LCP sticks were donated (in-kind) by the City of Calgary for use in this research project. Two (2) custom steel end plates were created to cap off either end of the test setup; one end plate includes a 2-inch tap at the bottom for water (i.e. filling and draining); one end plate includes a 1-inch tap at the top for bleeding air. See Figure 3.3. Three (3) 4-inch ports were added with Victaulic grooves to attach sealing assemblies for the acoustic sensors. The end plates are made of 1-inch steel and have cross bars welded on the surface to improve stability. The pipeline joints were welded, a fairly common practice in some pipelines. Welded joints were used in order to produce better acoustic transfer from pipe to pipe than would otherwise be the case. The design was modeled using computer software and confirmed to withstand loads in excess of 90 psi. 29 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 3.3(a): End plate with 2-inch tap (b): End plate with 1-inch tap In accordance with industry practices, 10mm (0.4 inch) pea gravel was acquired for pipe bedding. Enough gravel was acquired to place 4 inches below the pipe and 12 inches to the sides and top of the pipe following industry standards. With the goal of burying the PCCP sticks before the looming winter and to ensure the QA/QC measures were met, the following methodology was followed. 1. Each pipe stick was visually inspected and showed no signs of deterioration. 2. One end cap was welded to the bell end of one pipe; the second end cap was welded to the spigot end of another pipe. 3. A trench was excavated large enough to lay all three pipe sticks inside, approximately 69 feet in length, 11.5 feet in width, and 8 feet in depth. Worker access was required around the joints of the setup and the trench had to be deep enough to lay the pipes 4 feet below ground level (i.e. frost level). 4. The bottom of the trench was graded with a 4-degree slope so that air can rise to the high end and be purged from the pipes when filling with water; likewise, water can be drained out of the low end of the setup; a laser pointer was used to ensure the slope. 5. Half of the trench was bedded with the pea gravel and the other half was bedded using native soil (both industry practices); two bedding practices are incorporated for comparison. 6. Starting with the low end of the slope (i.e. water fill/drain end), a crane was used to lift each stick of PCCP and lay it into the trench. See Figure 3.4. 30 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 3.4: Crane-lifted PCCP 7. A tether (cable) line was passed through the pipes and through access ports in order to pull the fiber optic sensing cable at a later date; if the tether wire were to break prior to sensor installation, then a rigid “fishing” cable will be inserted through the pipe to pull the fiber optic cable. 8. The two pipe joints connecting the three PCCP sticks were externally welded for a stronger and water-tight seal. 9. All ports/taps on the end plates were capped in order to prevent infiltration into the pipes. 10. In order to protect the pipe setup from the oncoming winter and ensure safety at the site, the trench was fully backfilled using the excavated native soil. 11. Markers (i.e. stakes) were placed along the edges of the setup to mark the exact location of each stick of pipe. See Figure 3.5. Figure 3.5: PCCP stake positions Work resumed on the buried test setup once the Calgary winter had passed and weather conditions improved. The test setup was completely buried as a precautionary measure so two (2) large pits were excavated on either end of the setup to provide access to the pipes. In addition to the end pits, three (3) long pits were created on the top of the test pipe setup and a strip of outer mortar coating was removed to expose the prestressing wires. See Figure 3.6. 31 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Pit Pipe end access Prestressing wire Figure 3.6(a): Exposed pipe ends/pits (b): Pit window with exposed prestressing wire Instrumentation Description Acoustics A fiber sensor was passed through the setup and a hydrophone was inserted for comparison. The fiber sensor required careful fiber “splicing” onsite to route the optical pathways. Each splice was examined to ensure that the total light loss through each fiber did not exceed the limits. Various impact test strikes were performed to check the event locating accuracy of the AFO system. One wire was cut using bolt cutters, recorded and analyzed to ensure that the system was operational. See Figure 3.7. Figure 3.7(a): Fiber insertion at pipe end (b): Fiber splicing (c): Impact testing for AFO system Since the signals are affected by the pressure within the pipe, calibration was performed by generating wire breaks at different pressures and comparing the resulting data. 32 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Because the sensor is a distributed sensor, the initial portions of the signal were unaffected by the fact that the joints were welded. Later portions did start to show dispersion and attenuation at a slightly slower rate than would otherwise be the case. Since the ends of the pipes were not restrained by the welding, the wire breaks near the end caps were used as reference to make a comparison with breaks near welded joints. Volumetric Measurement In parallel with the wire cut tests, a volume test was performed to examine the loss of compression as prestressing energy was released. Specifically, a relation between the number of sequential wire cuts and the amount of additional water to maintain pressure was recorded. A specialized device was designed and built to maintain a constant pressure as wire cuts proceeded, see Figure 3.8. Figure 3.8(a): Constant pressure device at pipe end (b): Water reservoir The volume of water added to the pipe to maintain 62 psi versus the number of sequential wire cuts was recorded and mapped out. See Figure 3.9. A total of 4 liters (1.05 U.S. Gal) was required to maintain the pressure at 62 psi at the conclusion of all wire cuts. 33 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 3.9: Volume of water added vs. number of sequential wire cuts Test Procedures Cut Sequence Rationale Specially modified bolt cutters were used to manually cut the prestressing wires, as depicted in Figure 3.10. Other methods were initially examined; such as acid environment, electrically driven corrosion cells, and hypothermic shock. The amount of acid required to break hundreds of wires presented a serious hazard and so the method was discarded. The time required to corrode so many wires electrochemically also caused that method to be discarded. In the end, the bolt cutters provided satisfactory results. For typical in-service pipe, the propensity of the position of wire breaks to progress away from the source point—often a joint—assisted the investigators in making the decision to cut wires in the same manner progressing away from a joint. Earlier work (Bell and Paulson 2010) did indicate that as each wire breaks, the adjacent wires are exposed to a sudden increase in strain; an observation that supports the progression of breaks. Wires were cut in a systematic fashion (Figure 3.11) to control the displacement of prestressing energy over each individual PCCP spool. The loss of prestress energy was evident from the audible and visual separation of the prestressing wires after each cut. 34 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 3.10: Bolt cutters used to simulate wire breaks Figure 3.11: Wires cut in a systematic fashion Data Collection and Storage The fibers were routed to an onsite workstation (Figure 3.12) that housed the AFO data acquisition unit (DAQ). The DAQ controlled the whole system—it detected and recorded the acoustic events. The investigator’s engineers were onsite to oversee the setup and test the system to ensure that performance met or exceeded standards. Each time a wire was cut, the DAQ would detect and record the event. Wire break simulation experiments were performed on the 42-inch LCP in two phases separated by about Figure 3.12: Onsite workstation Figure 3.12: Onsite workstation 90 days. The objective was to collect data with a variety of levels of strain relief with each increasing wire break. After completion of the buried PCCP test facility (Figure 3.13), cuts started in July 2012 at Joint D1-D2 and moved South on Pipe D2, sequentially cutting 25 wires. A few days later cutting continued with another 25 wires, resuming the sequence at wire 26 to wire 50. In October, the investigator’s engineers counted out to wire 100 on Pipe D2 from Joint D1-D2. Starting with wire 100, wires were cut in sequence south to north to wire 51, meaning that wires were cut progressively moving toward the first group of 50 wires already cut. 35 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 3.13: Orientation of the buried PCCP test facility PIPE WALL ASSESSMENT DIP FACILITY Design of the Facility Five (5) spools of 12-inch ductile iron (DI) pipe were assembled to test the acoustic response of non-PCCP pipe. The earth displaced during the PCCP burial was used to cover the DI test setup and simulate the compaction of a buried pipeline. See Figure 3.14. Figure 3.14(a): 12-inch ductile iron pipe (b): Buried with earth displaced from PCCP test The spools were connected using four (4) different flange/clamp methods. Each method represented a difference in stiffness that can be further examined. Up to six (6) additional clamps were placed in succession to simulate an increase in hoop stiffness along one spool of DI pipe. See Figure 3.15. 36 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 3.15(a): Various joint connections (b): Addition of up to six (6) additional clamps Description of Instrumentation Ideally a fiber optic cable would be used to capture acoustic events. However, the spatial resolution of a fiber optic cable is constrained by the ability to measure the time of arrival of perturbations of light. A 1M resolution requires that the light be sampled at 100,000,000 (10E8) samples per second. To resolve a 1% change over a 1m length, the sampling would need to be at 10E10 samples per second. Currently, such a resolution is difficult to achieve. So instead, custom pulsers were installed on the pipe end caps to generate acoustic pulses and excite the pipe. An acoustic sensor was used to capture the response. Test Procedures The acoustic sensor (hydrophone) was passed through the pipe and recorded the pulses at different points to create an acoustic profile of the pipe. The pulser travelled concurrently a fixed distance from the hydrophone. See Figure 3.16. Figure 3.16: Example of test procedure 37 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. The pipe was then excavated at one location between joints, a clamp was added to the pipe, and the test procedure was performed again. Another clamp was then added and the test procedure performed again. This continued until a total of six (6) clamps were added. EXISTING IN-SITU MONITORING SYSTEMS In addition to the field-based destructive testing of buried PCCP conducted during the course of this project to collect controlled acoustic data associated with wire breaks, delaminations and other events preceding PCCP failure, existing in-situ systems were examined. PCCP owners around the world have invested billions into their PCCP assets and millions into condition assessment and monitoring of these assets. Overview of Monitoring Systems With over 5,000 wire breaks recorded to date, Pure Technologies possesses the only known existing database of spontaneous wire breaks in operating pipelines as detected with distributed fiber optic sensors. Some of the pipes monitored with fiber optic sensors over past years have been excavated and inspected, affording information as to the condition of pipes in which spontaneous wire breaks were detected. Importantly, this allowed the investigators to compare the results in the field with the output of models and algorithms developed from the buried, controlled test described above. The feedback loop created in this way improved the practical applicability of results from this work. Several participating utilities had expressed intent to perform additional validation(s) of AFO-monitored distressed pipe sections during the course of this project. These validations are planned to compare the buried, controlled test to field results for participating utility’s pipes. For these external investigation Pure Technologies will combine its proprietary external nondestructive, electromagnetic inspection tool with visual and sounding inspection to minimize disruption to the PCCP owner. The investigators have analyzed the empirical data from this project and have applied different methodologies to the existing data. Participant Support The investigators secured the participation of PCCP owners from across the United States and Canada. The monitored length of just the participant pipelines exceeds 120 miles over 19 separate installations. The investigators applied the mathematical methods and acoustic signal profiles characteristic of PCCP failure to the utility participant AFO data. All of the participant’s AFO data was investigated for mining. The investigators used prior validations to verify the mathematical models when feasible. The investigators had identified two well-controlled prior validations of AFO-monitored pipelines and secured the PCCP owners participation and contribution of the validation data to this project. Only these prior validations were counted as in-kind contributions to this project. PCCP owners without active AFO-monitored pipelines were also included as in-kind participants. PCCP owners have a long history of applying many different condition assessment and monitoring technologies to their pipelines with varying levels of success. The investigators have sought to create the most practically applicable AFO-based condition assessment technique 38 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. by involving PCCP owners throughout the project. Workshops were held with water utilities with PCCP in their systems (tens to hundreds and possibly thousands of miles) throughout the project duration. Workshops were held concurrently with major conferences favored by PCCP owners and operators, and the utility participants: AWWA Annual Conference and Exhibition (ACE) ASCE Pipelines AWWA Distribution System Symposium (DSS) The PCCP User Group is a utility-based group of approximately 50 members that meet periodically to discuss issues relevant to PCCP. The members have typically had pipeline failures or other issues and are the best source of information not available in open literature. The PCCP Users Group typically meets in conjunction with ASCE Pipelines each year. One of the project workshops was held in conjunction with the 2012 PCCP Users Group at ASCE Pipelines in Miami, FL. Participant Monitoring Systems The utilities that had committed to participating in this study all had a vested interest in furthering PCCP condition assessment through AFO monitoring to extend the service life of their PCCP infrastructure and more importantly to reduce the risk of catastrophic failures. Some utilities simply had PCCP in their systems and sought to provide guidance and direction for the scope and deliverables of this project. Other utilities had already been actively monitoring their PCCP using AFO for the purpose of identifying wire breaks and the associated lack of structural integrity. A third group not only had active AFO monitoring systems, but had committed to contributing prior and/or future AFO validation studies to this project. The participating utilities provided a wide variety of types and sizes of PCCP, environmental conditions in which PCCP had been buried, and pipe manufacturers. While the Foundation is focused on advancing the science of drinking water by providing utilities and drinking water suppliers with practical solutions to complex issues, PCCP has also been used widely in non-drinking water applications. Arizona Public Service Company (APS) operates 37 miles of PCCP transporting treated sewage effluent from a major sub-regional wastewater treatment plant to the Palo Verde Nuclear Generating Station. APS was committed to participating in this project. Howard County owns and operates approximately 20 miles of PCCP, of which approximately 7 miles is AFO monitored. Howard County regularly performs validations of wire breaks detected by the AFO system. In early February 2011 a total of seven pipes, including both single-wrapped and double-wrapped PCCP, were excavated and removed from the 36-inch Southwestern Transmission Main. This pipeline has been AFO-monitored since 2007. Pure Technologies has reported wire breaks from AFO monitoring on these pipes and the purpose of the validation is to confirm the locations and quantities of wire breaks reported. Certain acoustic data analysis methods or algorithms developed during this project can also be applied to the Southwestern Transmission Main AFO data and the field validation results used to test the performance of the algorithms. Figure 3.17 shows the excavation of this 36-inch pipeline on February 2, 2011. 39 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Field investigations were also performed on WSSC’s 96-inch Potomac Transmission Main. A rapid succession of wire break activity was reported to WSSC by Pure Technologies based on AFO monitoring. It is believed that this pipe was within hours or days of catastrophic failure when it was shut down and replaced. Figure 3.18 shows wire damage on the pipe exterior with a hollow and longitudinal crack in the corresponding interior location. AFO monitoring alerted WSSC to this highly distressed pipe prior to failure. Figure 3.17: Excavation of Howard County's 36-inch The condition of the pipe, mortar, and wires was carefully studied and southwestern transmission main documented before removal. The acoustic data analysis methods and algorithms developed for this research was applied to this pipeline and the prior field studies used to validate the research. The value of a portion of the field studies was contributed to this project by WSSC. Figure 3.18: Damage to WSSC's 96-inch Potomac transmission main The following is a list of all the participating utilities. Arizona Public Service Company Central Arizona Project City of Calgary City of London Dallas Water Utilities Howard County Department of Public Works Louisville Water Company 40 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Metropolitan Water District of Southern California Providence Water San Diego County Water Authority Tarrant Regional Water District Tucson Water Washington Suburban Sanitary Commission 41 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. ©2014 Water Research Foundation. ALL RIGHTS RESERVED. CHAPTER 4: RESULTS AND SIGNAL ANALYSIS FOR PCA PCCP DATA PRESENTATION OF ACOUSTIC TEST DATA Each successive wire break from the experimental test site in Calgary was recorded acoustically. An example of a raw signal from the fiber sensor is presented in Figure 4.1. Figure 4.1: Fiber sensor raw signal from experimental test site wire cut The wire break sensor data from the experiment appeared to adequately mimic fieldapplied FOC acoustic monitoring system data. The spectra of the fiber sensor and the hydrophone, installed for comparison, are shown in Figure 4.2. The similarity between the two was noted. 43 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 4.2: Fiber sensor and hydrophone data Observations and Analysis of PCCP Test Data The energy of the cuts was examined near the start of the cut, approximately the first 10 msec of the cut. Specifically, the ratio of energy in the high frequency range was examined (rather arbitrarily chosen as > 10 kHz) and the low frequency range (<10 kHz) changed with increasing number of wire cuts. A decent negative correlation was found for the high frequency energy of wire cuts performed in the pipe yard with wire cut number (r = -0.59), Figure 4.3. 44 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Wire Cut Number Figure 4.3: Pipe yard wire cut data However, the same trend was not observed with the wire cuts produced in the Middlesex County Utilities Authority (MCUA) study, Figure 4.4. Investigation later showed that these cuts were done using a cutting torch. Figure 4.4: MCUA wire cut data In both the pipe yard wire cuts and the MCUA wire cuts, a slight positive correlation was observed in the High Frequency Energy/Low Frequency Energy ratio (r = 0.318 and r = 0.347, respectively). See Figure 4.5 and Figure 4.6. 45 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 4.5: Pipe yard wire cut frequency ratio vs. wire cut Figure 4.6: MCUA wire cut frequency ratio vs. wire cut The measured acoustic output from each of the 100 wire cuts from the buried test setup is shown in Figure 4.7. 46 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 4.7: Measured acoustic output as a function of wire cuts The graph of root mean square (RMS) power, as shown in Figure 4.8, is the plot of the RMS power versus the second group of 50 wire cuts (i.e. wires 100 to 51). The extraction of values was done using max amplitude and max RMS power with a 5 msec window, using Adobe Audition. The observation was that the power changes significantly as the relaxation or recovery length of the wire was reduced. Figure 4.8: RMS average acoustic power vs. remaining wires The implication is that not only frequency/spectral characteristics can be used as a predictor in the change of pipe condition and approach to loss of structural integrity; acoustic power characteristics require further investigation as a predictor. ANALYSIS METHODS The general process was to extract certain features using mathematical analytical methods, apply each method to a group of data where a trend might exist, and examine the results. 47 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Short-Time Fourier Transform Ultimately, the Short-Time Fourier Transform (STFT) was selected as the most appropriate analysis method. The experimental acoustic time domain data was transformed to frequency domain for further analysis. Wavelet Analysis Analysis via wavelet transform was investigated as a means to glean additional useful information from the signal data. However, for the purposes of this study, in which the signal of a number of wire breaks are compared to each other, a simple wavelet transform was not expected to provide any additional information which was not given by other analyses. If, for example, the frequency content of the wire breaks changed as the damage on a particular pipe increased, the expectation was that this effect would manifest itself in the HEMP analysis as a correlation between the Half Energy frequency and the number of wire breaks. Since the frequency spectra of a number of wire breaks is being compared with wire cut signals and analyzed for trends with increasing number of breaks on a pipe, it was considered likely that any consistent changes in the frequency content of the wire cut signals would manifest themselves in our analysis of the frequency of half energy for each wire break. For example, if a scenario is imagined in which the frequency spectrum of each successive wire cut is different from the wire cuts previous, this would manifest as a correlation between the HEMP frequency and the wire cut number. Indeed, a wavelet analysis would also reveal this information, but a direct comparison of the frequency spectra obtained using a standard Fourier transform is simpler and should be equally effective in this case. A wavelet analysis attempting to find changes in the temporal position of certain frequencies within all the wire cuts, and comparing this information between cuts may be a next step if further analyses are to be done. However, the investigators have for several years been using the short-time Fourier transform to analyze data from wire breaks and other pipeline noise. The short-time Fourier transform is similar to a wavelet transform, in that it provides some temporal information as to the frequency content of the signal. But in the investigator’s experience using the short-time Fourier transform has not provided any indication of any obvious changes in the temporal distribution of frequencies in wire break signals as a pipe accrues more damage that would not be revealed by a HEMP analysis. Monte Carlo Analysis At this time, the value of Monte Carlo techniques to the research at hand are not clear. At this point, FFT, WFT and wavelet methods seem most appropriate. APPLICATION OF BEST CANDIDATE ANALYSIS METHOD TO REAL WORLD DATA Once the data was transformed to frequency domain, analysis continued. Selected Data From the participant supporters and database of existing in-situ monitoring system wire break data, WSSC, Ottawa, San Diego, Tucson, and Cutzamala were selected as having pipe 48 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. systems with wire break data most comparable to the experimental Calgary yard setup. These monitoring sites had pipes verified to have been in imminent failure when excavated. It should be noted that most of the select data sites are embedded cylinder pipe, whereas the Calgary test site is lined cylinder. In addition, differences in the field loading conditions, in particular, ratio of design pressure to operating pressure may impact the effectiveness of the analysis and comparison. Characteristics and Comparison of Results RMS Power Analysis First, an analysis of the average RMS power (amplitude analysis) was performed using data from the Calgary pipe yard, as well as with the selected database data. The average RMS power data appears to reveal some trends, however this is only clearly visible in the experimental pipe yard data. Initially the average RMS power had a slight increase with additional wire cuts. However, after a certain number of wires were cut, the average RMS power decreased substantially as each successive wire was cut. This trend was observed with pipe D2 as shown in Figure 4.9. RMS average acoustic power released vs. number of remaining wires ‐50 ‐52 ‐54 ‐58 ‐60 ‐62 RMS Power in dB ‐56 ‐64 ‐66 ‐68 ‐70 50 45 40 35 30 25 20 15 10 5 0 Number of Remaining Wires Figure 4.9: Average RMS power from pipe yard D2 This plot only shows the second set of cuts (51–100) because these were done on the same day and in the same direction. The first set of cuts on pipe D2 (1–50) were performed on a different day and started at the other end of the pipe, so combining them on the same plot would not yield the best comparison of signals. 49 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Also compiled was a plot showing all the cuts at once, see Figure 4.10. As observed, the first set of cuts (1–50) was much noisier than the second set (50–100). This may have had something to do with background noise or adjusting of the hardware. In any case, cuts 50–100 were much cleaner and yielded a more discernible trend. Figure 4.10: Average RMS power from pipe yard D2 with all cuts A similar trend was observed in pipe D3 as shown in Figure 4.11. Only 50 cuts were performed on pipe D3, so that is why that plot only goes from 1–50. 50 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. D3 Average RMS Power ‐77 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 ‐77.1 ‐77.2 RMS Power (dB) ‐77.3 ‐77.4 ‐77.5 ‐77.6 ‐77.7 ‐77.8 ‐77.9 ‐78 Wire Cut Number Figure 4.11: Average RMS power from pipe yard D3 Figure 4.12 depicts the first 20 cuts performed on pipes D2 starting from the D1 Joint, the first 20 cuts starting from the D3 joint, and the first 20 cuts on D3 on the same plot for comparison. Figure 4.12: RMS power from pipe yard D2 and D3 51 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. The energy of the cuts on pipe D3 were very consistent, but were more varied on pipe D2. Some of the first few cuts done on D2 were not reliable due to hardware adjustment, so the data appears skewed for the “D2 from D1 joint” data. The first 20 cuts on D2 from the D3 joint were better and showed the similar upward and then downward trend. When the analysis was also performed on data from the monitoring site database, a similar trend was observed. However, as the sample size was much smaller for the in-situ database data, it is difficult to confirm the correlation with certainty. Data from WSSC, Ottawa, San Diego, and Tucson is illustrated in Figure 4.13, Figure 4.14, Figure 4.15, and Figure 4.16, respectively. Average RMS Power vs. Wire Break Number ‐ WSSC 0 0 1 2 3 4 5 6 7 8 ‐10 ‐20 Energy (dB) ‐30 y = ‐0.5985x2 + 8.5645x ‐ 75.1 R² = 0.9884 ‐40 ‐50 ‐60 ‐70 ‐80 Wire Break Number Figure 4.13: Average RMS power from WSSC AFO site 52 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. 9 10 Average RMS Power vs. Wire Break Number ‐ Ottawa ‐58 0 2 4 6 8 10 12 14 ‐58.5 Energy (dB) y = 0.047x ‐ 59.722 R² = 0.065 ‐59 ‐59.5 ‐60 ‐60.5 Wire Break Number Figure 4.14: Average RMS power from Ottawa AFO site Average RMS Power vs. Wire Break Number ‐ San Diego ‐36.5 0 2 4 6 8 10 ‐37 ‐37.5 Energy (dB) ‐38 ‐38.5 ‐39 y = ‐0.1404x ‐ 37.885 R² = 0.2149 ‐39.5 ‐40 ‐40.5 ‐41 Wire Break Number Figure 4.15: Average RMS power from San Diego AFO site 53 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. 12 14 Average RMS Energy vs. Wire Break Number Tucson 1 Wire Break Number ‐10 5 7 9 11 13 15 17 19 21 ‐12 ‐14 Energy (dB) ‐16 ‐18 ‐20 ‐22 ‐24 ‐26 ‐28 y = ‐0.2435x2 + 6.712x ‐ 65.753 R² = 0.5567 ‐30 Figure 4.16: Average RMS power from Tucson AFO site The AFO site in Cutzamala, Mexico has several pipes with a large number of breaks (i.e. more than 50). This is one the largest number of AFO breaks on single pipes contained within the database. The RMS power plot was performed on one such pipe that was excavated and confirmed to be damaged. See Figure 4.17. Figure 4.17: Average RMS power from Cutzamala AFO site 54 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Here, there appears to be no correlation with wire break number and RMS power. It was hypothesized that the breaks on this particular pipe were due to hydrogen embrittlement (HE). Since HE breaks do not reduce the integrity of the pipes as much as other types of wire breaks, it extends that no change in RMS power may be seen. This phenomenon, if confirmed, may prove to be beneficial as a random distribution of RMS power could potentially help identify HE vs. corrosion-related wire breaks at AFO sites. In general, RMS energy appears to have greater sensitivity to wire cuts and field-collected data although specific and detailed differences in manufacturing of PCCP may influence effectiveness of post processing. The correlation of average RMS power to wire breaks appears promising to be able to extend additional signal processing capabilities to an existing dataset. Utilities that have been monitoring for sound should have a high enough degree of signal fidelity to facilitate analysis, assuming the bandwidth of current practice in fiber optic is sufficient. Noting that the currently available bandwidth is typically from a few Hz to more than 30 kHz, there is an expectation that current practice in acquisition need not be altered. To verify this, the duration of acoustic event captured surrounding each wire break was lengthened to 10 seconds to potentially allow very low frequency resonances to be identified. However, no additional useful information was captured from the longer time interval. HEMP Analysis Next, a peak frequency analysis was performed. This half energy (HEMP) analysis was performed on the experimental pipe yard data and selected AFO sites. The HEMP analysis from Day 2 in the pipe yard showed a slight positive correlation between the change in median frequency and wire cut number, and Day 3 in the pipe yard showed a moderate negative correlation between the change in median frequency and wire cut number. See Figure 4.18 and Figure 4.19. 55 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. HEMP Frequency vs. Wire Cut Number ‐ D2 30000 HEMP Frequency (Hz) 25000 20000 15000 10000 y = 267.94x ‐ 1693.2 R² = 0.1204 5000 0 50 55 60 65 70 75 Wire Cut Number Figure 4.18: HEMP analysis from pipe yard D2 HEMP Frequency vs. Wire Cut Number ‐ D3 25000 HEMP Frequency (Hz) 20000 15000 10000 y = ‐180.88x + 16737 R² = 0.2672 5000 0 0 5 10 15 20 25 30 35 40 45 Wire Cut Number Figure 4.19: HEMP analysis from pipe yard D3 Neither trend was especially observed in the selected data from other pipe sites, although this could be in part because the sample size of wire breaks is so much smaller for the AFO sites. See Figure 4.20, Figure 4.21, Figure 4.22, and Figure 4.23 for HEMP analysis for sites at WSSC, Ottawa, San Diego, and Tucson, respectively. 56 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. HEMP Frequency vs. Wire Break Number ‐ WSSC 18000 16000 HEMP Frequency (Hz) 14000 12000 10000 8000 y = ‐174.74x + 13066 R² = 0.032 6000 4000 2000 0 0 1 2 3 4 5 6 7 8 Wire Break Number Figure 4.20: HEMP analysis from WSSC AFO site HEMP Frequency vs. Wire Break Number ‐ Ottawa 18000 16000 HEMP Frequency (Hz) 14000 12000 10000 y = ‐102.25x + 15461 R² = 0.0938 8000 6000 4000 2000 0 0 2 4 6 8 10 Wire Break Number Figure 4.21: HEMP analysis from Ottawa AFO site 57 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. 12 14 HEMP Frequency vs. Wire Break Number ‐ San Diego 14000 12000 HEMP Frequency (Hz) 10000 8000 6000 4000 y = 38.027x + 8662.5 R² = 0.0158 2000 0 0 2 4 6 8 10 12 14 Wire Break Number Figure 4.22: HEMP analysis from San Diego AFO site Tucson 1 HEMP Frequency vs. Wire Break Number 30000 HEMP Frequency (Hz) 25000 20000 y = 95.103x + 11767 R² = 0.0098 15000 10000 5000 0 0 2 4 6 8 10 12 14 16 18 Number of Wire Breaks Figure 4.23: HEMP analysis from Tucson AFO site HEMP analysis from FFT data initially seemed to be useful based on data from the SDCWA failures. However, when it was applied to a more controlled and broader spectrum of results, it does not appear useful due to lack of any sort of consistent correlation. 58 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. CHAPTER 5: PIPE WALL ASSESSMENT (NON-PCCP) RESULTS PRESENTATION AND ANALYSIS OF PWA TEST DATA In the DIP experimental setup, the pulse generated by the pulser was received by the roving hydrophone. The time interval between the generation of the pulse and the detection of the pulse at 10 feet was plotted versus the pulser position. See Figure 5.1. Each pipe joint clearly appeared in the data as a change in pipe hoop stiffness. The largest variations appeared at restrained flex couplings, with smaller effects at the flexible sleeve coupling and flanged joints. Figure 5.1: Pipe wall assessment data with various pipe joint connections A series of clamps was then added, with the test procedure performed and the data recorded between each successive clamp addition. The flight time for no clamps, two (2) clamps, four (4) clamps, and six (6) clamps was plotted verses pipe position. See Figure 5.2. Again, the data clearly showed the increase in hoop stiffness as each clamp was added. 59 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. Figure 5.2: Pipe wall assessment data, illustrating effect of additional clamps The ability to successfully distinguish between areas of varying stiffness may be useful in identifying areas of deterioration in non-PCCP. Failure mechanisms such as uniform metal loss or longitudinal cracking would appear as sections of diminished stiffness. These failure mechanisms are highly localized and require a technique with sufficient resolution to distinguish varying levels of hoop stiffness in less than a pipe length. Highly localized variations in stiffness (e.g. reduction is wall thickness) were not investigated as would be the case for most corrosion or pitting in iron piping systems, but this technique appears promising for the pipe wall assessment of non-PCCP. 60 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. CHAPTER 6: SUMMARY AND CONCLUSIONS OF THE RESEARCH The owners or users of PCCP currently live with the nagging concern or fear that continuing degradation of their buried pipe will cause loss of continuity of service, property damage or, in the worst case, loss of life. The newspapers and television news are periodically smattered with the devastation that can be wrought by such a failure. The risk of a failure is the product of the likelihood or probability of failure and the consequence or cost of that failure. Little can be done to manage the consequence of a failure since water delivery is essential and right of ways are increasingly more urbanized as a result of the available water supply. The only thing that can be done is to manage the likelihood of failure by improving the transformation of direct structural condition (acoustic) data to actionable information. Based on the earlier work by the project Principal Co-Investigators, it appeared that existing technology had sufficient resolution to collect data in the time domain with sufficient resolution to detect trends in pipe condition (Travers 1994, Bell et al. 2009). It did not appear that advancement in technology was necessary, just improvement in analysis, collection of pedigreed and confirmed baseline data for use in the development of the analytical methods, and finally field verification of the methodology. A test setup utilizing three lengths of LCP PCCP was installed in Calgary to experiment with wire breaks and the resultant acoustic signals. The raw signal was processed using Fourier transforms and the ensuring spectra data was analyzed for average RMS power and peak frequency (HEMP) analysis. While the HEMP analysis did not prove useful, the average RMS power showed promise for correlating the signal amplitude with the number of broken wires. A general trend could be seen in RMS amplitude as prestressing wires wraps were successively cut. Data from the real-world monitored pipes were examined to see if the same pattern was evident which showed some evidence of such; however, the samples sizes were not large enough to confirm or deny the overall trend. The practice of managing PCCP risk may now be simplified. We are “fortunate” with PCCP that 1) the prestressed high strength wires are the primary structural members of the pipe design (if you monitor and manage wire breaks you can help monitor and manage pipe integrity and likelihood of failure), and 2) when a wire break occurs, the energy release provides a method of excitation by which the integrity or structural response can be measured. Fundamentally, this is what all condition assessment methods do; excite, measure the response and then analysis of data provides information for action. For PCCP owners, the deterioration can be monitored as the wires break and excite the pipe structure and the structural condition assessed. Bell and Paulson (2010) coined the phrase, “Noisy Pipes are not Happy Pipes.” In essence, this was the first step in using acoustic data for condition assessment. It is similar to using your hand to determine if you have a fever. The new method should effectively be a “thermometer” for the condition of the pipe. In its optimal result, PCCP owners would be able to operate their pipelines right to the brink of failure prior to taking them out of service for repair or rehabilitation. In this manner, rehabilitation would be planned and capital expenditures optimized. Further down the road, it may be possible to use the same fundamental processes to evaluate other pipe materials. In order to do this, new technology for excitation and response may be necessary since other pipe materials do not have the advantage of excitation by wire breaks. Having said that, the first step is to develop the methods using PCCP and then move the process along. Since the correlation of average RMS power and wire breaks was found, it can be immediately applied to all pipelines where AFO data exist, including retrospectively. If a pattern 61 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. in RMS amplitude such as that seen from one of the test pipes becomes evident in any monitored pipes, this will be communicated with the pipeline owners to take appropriate investigative measures. In the long term, it may be possible to conduct analysis in real time to allow pipe condition to be understood as a continuum rather than single data point of condition or the result of failures. 62 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. CHAPTER 7: FUTURE RESEARCH SUGGESTIONS Perform further research with wavelet analysis to determine if any meaningful data can be extracted beyond what can be determined from FFT or STFT. Further investigate the value of Monte Carlo techniques to the research at hand. Investigate if the time between wire breaks, or wire reliability trending, could prove useful in predicting time to imminent failure. Perform additional experimentation with different field loading conditions, in particular, the ratio of design pressure to operating pressure, to determine the effect on acoustic signal processing. Investigate further the effect of hydrogen embrittlement on the distribution of average RMS power vs. wire cuts/breaks. This phenomenon, if confirmed, may prove to be beneficial as a random distribution of RMS power could potentially help identify HE vs. corrosionrelated wire breaks at AFO sites. In PWA, investigate highly localized variations in stiffness to further qualify this method in real-world situations (e.g. pitting or corrosion). 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ABBREVIATIONS AE Acoustic event ACE Annual Conference and Exhibition AFO Acoustic Fiber Optic AM Amplitude modulation APS Arizona Public Service Company ASCE American Society of Civil Engineers ASME American Society of Mechanical Engineers ASTM American Society for Testing and Materials AWWA American Water Works Association DAQ Data acquisition unit dB Decibels DFT Discrete Fourier transform DI Ductile iron DIP Ductile iron pipe DSS Distribution System Symposium DWT Discrete wavelet transform ECP Embedded cylinder pipe ed. editor FFT Fast Fourier transform FM Frequency modulation FOC Fiber-optic cable ft. feet Gal Gallon gm gram HDPE High-density polyethylene HE Hydrogen embrittlement 71 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. HEMP Peak frequency analysis Hz Hertz IE Impact echo IEEE Institute of Electrical Engineers kHz Kilohertz lb pounds LCP Lined cylinder pipe m Meters M Million ML Maximum likelihood mm Millimeters MCUA Middlesex County Utilities Authority msec milliseconds NACE NACE International, formerly National Association of Corrosion Engineers PCA Passive condition assessment PCCP Prestressed concrete cylinder pipe PSD Power spectral density psi Pounds per square inch PVC Polyvinyl chloride PWA Pipe wall assessment QA/QC Quality assurance/quality control RMS Root mean square ROC Receiver operating characteristic SDCWA San Diego County Water Authority 72 ©2014 Water Research Foundation. ALL RIGHTS RESERVED. STFT Short-Time Fourier Transform U.S. United States vs. versus WFT Windowed Fourier transform WSSC Washington Suburban Sanitary Commission 73 ©2014 Water Research Foundation. ALL RIGHTS RESERVED.