United States Office of Research and EPA/540/R-06/006 Environmental Protection Development February 2006 Agency Washington, DC 20460 Innovative Technology Verification Report XRF Technologies for Measuring Trace Elements in Soil and Sediment Xcalibur ElvaX XRF Analyzer - oSto s c,f. J^W^ ------- EPA/540/R-06/006 February 2006 Innovative Technology Verification Report Xcalibur ElvaX XRF Analyzer Prepared by Tetra Tech EM Inc. Cincinnati, Ohio 45202-1072 Contract No. 68-C-00-181 Task Order No. 42 Dr. Stephen Billets Characterization and Monitoring Branch Environmental Sciences Division Las Vegas, Nevada 89193-3478 National Exposure Research Laboratory Office of Research and Development U.S. Environmental Protection Agency ------- Notice This document was prepared for the U.S. Environmental Protection Agency (EPA) Superfund Innovative Technology Evaluation Program under Contract No. 68-C-00-181. The document has been subjected to the Agency's peer and administrative review and has been approved for publication as an EPA document. Mention of corporation names, trade names, or commercial products does not constitute endorsement or recommendation for use. 11 ------- Foreword The U.S. Environmental Protection Agency (EPA) is charged by Congress with protecting the nation's natural resources. Under the mandate of national environmental laws, the Agency strives to formulate and implement actions leading to a compatible balance between human activities and the ability of natural systems to support and nurture life. To meet this mandate, EPA's Office of Research and Development (ORD) provides data and scientific support that can be used to solve environmental problems, build the scientific knowledge base needed to manage ecological resources wisely, understand how pollutants affect public health, and prevent or reduce environmental risks. The National Exposure Research Laboratory is the Agency's center for investigation of technical and management approaches for identifying and quantifying risks to human health and the environment. Goals of the laboratory's research program are to (1) develop and evaluate methods and technologies for characterizing and monitoring air, soil, and water; (2) support regulatory and policy decisions; and (3) provide the scientific support needed to ensure effective implementation of environmental regulations and strategies. EPA's Superfund Innovative Technology Evaluation (SITE) Program evaluates technologies designed for characterization and remediation of contaminated Superfund and Resource Conservation and Recovery Act (RCRA) sites. The SITE Program was created to provide reliable cost and performance data to speed acceptance and use of innovative remediation, characterization, and monitoring technologies by the regulatory and user community. Effective monitoring and measurement technologies are needed to assess the degree of contamination at a site, provide data that can be used to determine the risk to public health or the environment, and monitor the success or failure of a remediation process. One component of the EPA SITE Program, the Monitoring and Measurement Technology (MMT) Program, demonstrates and evaluates innovative technologies to meet these needs. Candidate technologies can originate within the federal government or the private sector. Through the SITE Program, developers are given an opportunity to conduct a rigorous demonstration of their technologies under actual field conditions. By completing the demonstration and distributing the results, the Agency establishes a baseline for acceptance and use of these technologies. The MMT Program is managed by ORD's Environmental Sciences Division in Las Vegas, Nevada. Gary Foley, Ph.D. Director National Exposure Research Laboratory Office of Research and Development in ------- Abstract The Elvatech, Ltd. ElvaX (ElvaX) x-ray fluorescence (XRF) analyzer distributed in the United States by Xcalibur XRF Services (Xcalibur), was demonstrated under the U.S. Environmental Protection Agency (EPA) Superfund Innovative Technology Evaluation (SITE) Program. The field portion of the demonstration was conducted in January 2005 at the Kennedy Athletic, Recreational and Social Park (KARS) at Kennedy Space Center on Merritt Island, Florida. The demonstration was designed to collect reliable performance and cost data for the ElvaX analyzer and seven other commercially available XRF instruments for measuring trace elements in soil and sediment. The performance and cost data were evaluated to document the relative performance of each XRF instrument. This innovative technology verification report describes the objectives and the results of that evaluation and serves to verify the performance and cost of the ElvaX analyzer. Separate reports have been prepared for the other XRF instruments that were evaluated as part of the demonstration. The objectives of the evaluation included determining each XRF instrument's accuracy, precision, sample throughput, and tendency for matrix effects. To fulfill these objectives, the field demonstration incorporated the analysis of 326 prepared samples of soil and sediment that contained 13 target elements. The prepared samples included blends of environmental samples from nine different sample collection sites as well as spiked samples with certified element concentrations. Accuracy was assessed by comparing the XRF instrument's results with data generated by a fixed laboratory (the reference laboratory). The reference laboratory performed element analysis using acid digestion and inductively coupled plasma - atomic emission spectrometry (ICP-AES), in accordance with EPA Method 3 05 OB/601 OB, and using cold vapor atomic absorption (CVAA) spectroscopy for mercury only, in accordance with EPA Method 7471 A. The ElvaX is a portable bench-top energy-dispersive XRF analyzer. The ElvaX is capable of detecting elements from sodium through plutonium and can be applied in the jewelry, metallurgy, customs, forensics, medical diagnostics, food testing, and environmental testing markets. The ElvaX can be used for qualitative or quantative analysis of metal alloys, liquid food, and biological samples. The ElvaX can analyze liquids and powders as well as samples deposited on surfaces or filters. The ElvaX analyzer system includes two primary components: an XRF spectrometer and a personal computer. The XRF spectrometer contains a 5-watt x-ray tube excitation source with tungsten, titanium, or rhodium as the anode target material and with an adjustable 4- to 50-kilovolt power supply. The detector is a Peltier-cooled, solid-state silicon-PiN diode with 180-electron volt resolution. The XRF spectrometer may be set up in the field but must be in a stable environment. No portable battery systems are currently available for the ElvaX spectrometer. A personal computer (laptop) with Microsoft Windows Millennium Editionฎ software is used to operate the XRF spectrometer and specifically to select x-ray tube parameters, store data, and provide radiation safety. The laptop is also used to display the x-ray spectrum and to process the data. Some examples of data processing steps included automatic peak search, overlapped peak deconvolution, background removal, automatic element identification, and background subtraction. This report describes the results of the evaluation of the ElvaX analyzer based on the data obtained during the demonstration. The method detection limits, accuracy, and precision of the instrument for each of the 13 target analytes are presented and discussed. The cost of element analysis using the ElvaX analyzer is compiled and compared to both fixed laboratory costs and average XRF instrument costs. IV ------- Contents Chapter Page Notice ii Foreword iii Abstract iv Acronyms, Abbreviations, and Symbols x Acknowledgements xiv 1.0 INTRODUCTION 1 1.1 Organization of this Report 1 1.2 Description of the SITE Program 2 1.3 Scope of the Demonstration 2 1.4 General Description of XRF Technology 3 1.5 Properties of the Target Elements 4 1.5.1 Antimony 5 1.5.2 Arsenic 5 1.5.3 Cadmium 5 1.5.4 Chromium 5 1.5.5 Copper 5 1.5.6 Iron 5 1.5.7 Lead 6 1.5.8 Mercury 6 1.5.9 Nickel 6 1.5.10 Selenium 6 1.5.11 Silver 7 1.5.12 Vanadium 7 1.5.13 Zinc 7 2.0 FIELD SAMPLE COLLECTION LOCATIONS 9 2.1 Alton Steel Mill Site 9 2.2 Burlington Northern-ASARCO Smelter Site 11 2.3 Kennedy Athletic, Recreational and Social Park Site 11 2.4 Leviathan Mine Site 12 2.5 Navy Surface Warfare Center, Crane Division Site 12 2.6 Ramsay Flats-Silver Bow Creek Site 13 2.7 Sulphur Bank Mercury Mine Site 13 2.8 Torch Lake Superfund Site 14 2.9 Wickes Smelter Site 14 3.0 FIELD DEMONSTRATION 15 3.1 Bulk Sample Processing 15 3.1.1 Bulk Sample Collection and Shipping 15 3.1.2 Bulk Sample Preparation and Homogenization 15 3.2 Demonstration Samples 17 3.2.1 Environmental Samples 17 3.2.2 Spiked Samples 17 3.2.3 Demonstration Sample Set 17 ------- Contents (Continued) Chapter Page 3.3 Demonstration Site and Logistics 20 3.3.1 Demonstration Site Selection 20 3.3.2 Demonstration Site Logistics 20 3.3.3 EPA Demonstration Team and Developer Field Team Responsibilities 21 3.3.4 Sample Management During the Field Demonstration 21 3.3.5 Data Management 22 4.0 EVALUATION DESIGN 23 4.1 Evaluation Objectives 23 4.2 Experimental Design 23 4.2.1 Primary Objective 1 - Method Detection Limits 24 4.2.2 Primary Objective 2 -Accuracy 25 4.2.3 Primary Objective 3 - Precision 26 4.2.4 Primary Objective 4 - Impact of Chemical and Spectral Interferences 27 4.2.5 Primary Objective 5 - Effects of Soil Characteristics 28 4.2.6 Primary Objective 6 - Sample Throughput 28 4.2.7 Primary Objective 7 -Technology Costs 28 4.2.8 Secondary Objective 1 - Training Requirements 28 4.2.9 Secondary Objective 2 - Health and Safety 29 4.2.10 Secondary Objective 3 - Portability 29 4.2.11 Secondary Objective 4 - Durability 29 4.2.12 Secondary Objective 5 -Availability 29 4.3 Deviations from the Demonstration Plan 29 5.0 REFERENCE LABORATORY 31 5.1 Selection of Reference Methods 31 5.2 Selection of Reference Laboratory 32 5.3 QA/QC Results for Reference Laboratory 33 5.3.1 Reference Laboratory Data Validation 33 5.3.2 Reference Laboratory Technical Systems Audit 34 5.3.3 Other Reference Laboratory Data Evaluations 34 5.4 Summary of Data Quality and Usability 36 6.0 TECHNOLOGY DESCRIPTION 39 6.1 General Description 39 6.2 Instrument Operations during the Demonstration 39 6.2.1 Setup and Calibration 39 6.2.2 Demonstration Sample Processing 40 6.3 General Demonstration Results 41 6.4 Contact Information 41 VI ------- Contents (Continued) Chapter Page 7.0 PERFORMANCE EVALUATION 43 7.1 Primary Objective 1 - Method Detection Limits 43 7.2 Primary Objective 2 - Accuracy and Comparability 46 7.3 Primary Objective 3 - Precision 52 7.4 Primary Obj ective 4 - Impact of Chemical and Spectral Interferences 55 7.5 Primary Objective 5 - Effects of Soil Characteristics 55 7.6 Primary Objective 6 - Sample Throughput 59 7.7 Primary Objective 7 - Technology Costs 59 7.8 Secondary Objective 1 - Training Requirements 59 7.9 Secondary Objective 2 -Health and Safety 59 7.10 Secondary Objective 3 - Portability 60 7.11 Secondary Objective 4 - Durability 60 7.12 Secondary Objective 5 -Availability 60 8.0 ECONOMIC ANALYSIS 61 8.1 Equipment Costs 61 8.2 Supply Costs 61 8.3 Labor Costs 62 8.4 Comparison of XRF Analysis and Reference Laboratory Costs 63 9.0 SUMMARY OF TECHNOLOGY PERFORMANCE 65 10.0 REFERENCES 71 APPENDICES Appendix A: Appendix B: Appendix C: Appendix D: Appendix E: Verification Statement Developer Discussion Data Validation Summary Report Developer and Reference Laboratory Data Statistical Data Summaries vn ------- Contents (Continued) TABLES Page 1-1 Participating Technology Developers and Instruments 1 2-1 Nature of Contamination in Soil and Sediment at Sample Collection Sites 10 2-2 Historical Analytical Data, Alton Steel Mill Site 11 2-3 Historical Analytical Data, BN-ASARCO Smelter Site 11 2-4 Historical Analytical Data, KARS Park Site 11 2-5 Historical Analytical Data, Leviathan Mine Site 12 2-6 Historical Analytical Data, NSWC Crane Division-Old Burn Pit 13 2-7 Historical Analytical Data, Ramsay Flats-Silver Bow Creek Site 13 2-8 Historical Analytical Data, Sulphur Bank Mercury Mine Site 14 2-9 Historical Analytical Data, Torch Lake Superfund Site 14 2-10 Historical Analytical Data, Wickes Smelter Site-Roaster Slag Pile 14 3-1 Concentration Levels for Target Elements in Soil and Sediment 18 3-2 Number of Environmental Sample Blends and Demonstration Samples 19 3-3 Number of Spiked Sample Blends and Demonstration Samples 19 4-1 Evaluation Objectives 24 5-1 Number of Validation Qualifiers 35 5-2 Percent Recovery for Reference Laboratory Results in Comparison to ERA Certified Spike Values for Blends 46 through 70 37 5-3 Precision of Reference Laboratory Results for Blends 1 through 70 38 6-1 Xcalibur ElvaX XRF Analyzer Technical Specifications 40 7-1 Evaluation of Sensitivity - Method Detection Limits for the Xcalibur ElvaX 44 7-2 Comparison of Mean ElvaX MDLs to All-Instrument Mean MDLs and EPA Method 6200 Data 46 7-3 Evaluation of Accuracy - Relative Percent Differences versus Reference Laboratory Data for the Xcalibur ElvaX 48 7-4 Summary of Correlation Evaluation forthe ElvaX 50 7-5 Evaluation of Precision - Relative Standard Deviations for the Xcalibur ElvaX 53 7-6 Evaluation of Precision - Relative Standard Deviations for the Reference Laboratory versus the ElvaX and All Demonstration Instruments 54 7-7 Effects of Interferent Elements on the RPDs (Accuracy) for Other Target Elements for the Xcalibur ElvaX 56 7-8 Effect of Soil Type on the RPDs (Accuracy) for Target Elements, Xcalibur ElvaX 57 8-1 Equipment Costs 61 8-2 Time Required to Complete Analytical Activities 62 8-3 Comparison of XRF Technology and Reference Method Costs 64 9-1 Summary of Xcalibur ElvaX Performance - Primary Objectives 66 9-2 Summary of Xcalibur ElvaX Performance - Secondary Objectives 68 Vlll ------- Contents (Continued) FIGURES Page 1-1 The XRF Process 4 3-1 Bulk Sample Processing Diagram 16 3-2 KARS Park Recreation Building 20 3-3 Work Areas for the XRF Instruments in the Recreation Building 21 3-4 Visitors Day Presentation 21 3-5 Sample Storage Room 22 6-1 ElvaX XRF Analyzer Set Up for Benchtop Analysis 39 6-2 Xcalibur Technician Preparing Samples for Analysis 41 6-3 Instrument Setup during the Field Demonstration 41 7-1 Linear Correlation Plot for ElvaX Showing High Correlation for Nickel 49 7-2 Linear Correlation Plot for ElvaX Showing High Data Variability for Silver 51 8-1 Comparison of Activity Times for the ElvaX versus Other XRF Instruments 63 9-1 Method Detection Limits (sensitivity), Accuracy, and Precision of the ElvaX in Comparison to the Average of All Eight XRF Instruments 69 ------- Acronyms, Abbreviations, and Symbols (ig Micrograms (iA Micro-amps AC Alternating current ADC Analog to digital converter Ag Silver Am Americium ARDL Applied Research and Development Laboratory, Inc. As Arsenic ASARCO American Smelting and Refining Company BN Burlington Northern C Celsius Cd Cadmium CFR Code of Federal Regulations cps Counts per second CPU Central processing unit Cr Chromium CSV Comma-separated value Cu Copper CVAA Cold vapor atomic absorption EDXRF Energy dispersive XRF EDD Electronic data deliverable EPA U.S. Environmental Protection Agency ERA Environmental Research Associates ESA Environmental site assessment ESD Environmental Sciences Division ETV Environmental Technology Verification (Program) eV Electron volts Fe Iron FPT Fundamental Parameters Technique FWHM Full width of peak at half maximum height GB Gigabyte Hg Mercury Hz Hertz ------- Acronyms, Abbreviations, and Symbols (Continued) ICP-AES Inductively coupled plasma-atomic emission spectrometry ICP-MS Inductively coupled plasma-mass spectrometry IR Infrared ITVR Innovative Technology Verification Report KARS Kennedy Athletic, Recreational and Social (Park) keV Kiloelectron volts kg Kilograms KSC Kennedy Space Center kV Kilovolts LEAP Light Element Analysis Program LiF Lithium fluoride LIMS Laboratory information management system LOD Limit of detection mA Milli-amps MB Megabyte MBq Mega Becquerels MCA Multi-channel analyzer mCi Millicuries MDL Method detection limit mg/kg Milligrams per kilogram MHz Megahertz mm Millimeters MMT Monitoring and Measurement Technology (Program) Mo Molybdenum MS Matrix spike MSB Matrix spike duplicate NASA National Aeronautics and Space Administration NELAC National Environmental Laboratory Accreditation Conference NERL National Exposure Research Laboratory Ni Nickel NIOSH National Institute for Occupational Safety and Health NIST National Institute for Standards and Technology NRC Nuclear Regulatory Commission NSWC Naval Surface Warfare Center ORD Office of Research and Development OSWER Office of Solid Waste and Emergency Response XI ------- Acronyms, Abbreviations, and Symbols (Continued) P Phosphorus Pb Lead PC Personal computer PDA Personal digital assistant PCB Polychlorinated biphenyls Pd Palladium PE Performance evaluation PeT Pentaerythritol ppb Parts per billion ppm Parts per million Pu Plutonium QA Quality assurance QAPP Quality assurance project plan QC Quality control r2 Correlation coefficient RCRA Resource Conservation and Recovery Act Rh Rhodium RPD Relative percent difference RSD Relative standard deviation %RSD Percent relative standard deviation SAP Sampling and analysis plan SBMM Sulphur Bank Mercury Mine Sb Antimony Se Selenium Si Silicon SITE Superfund Innovative Technology Evaluation SOP Standard operating procedure SRM Standard reference material SVOC Semivolatile organic compound TAP Thallium acid phthalate Tetra Tech Tetra Tech EM Inc. Ti Titanium TSA Technical systems audit TSP Total suspended particulates TXRF Total reflection x-ray fluorescence spectroscopy U Uranium USFWS U.S. Fish and Wildlife Service xn ------- Acronyms, Abbreviations, and Symbols (Continued) V Vanadium V Volts VOC Volatile organic compound W Watts WDXRF Wavelength-dispersive XRF WRS Wilcoxon Rank Sum XRF X-ray fluorescence Zn Zinc Xlll ------- Acknowledgements This report was co-authored by Dr. Greg Swanson and Dr. Mark Colsman of Tetra Tech EM Inc. The authors acknowledge the advice and support of the following individuals in preparing this report: Dr. Stephen Billets and Mr. George Brilis of the U.S. Environmental Protection Agency's National Exposure Research Laboratory; Ronald Williams of Xcalibur XRF Services, Inc. and Dr. Victor Martyniuk of Elvatech, Ltd.; and Dr. Jackie Quinn of the National Aeronautics and Space Administration (NASA), Kennedy Space Center (KSC). The demonstration team also acknowledges the field support of Michael Deliz of NASA KSC and Mark Speranza of Tetra Tech NUS, the consultant program manager for NASA. xiv ------- Chapter 1 Introduction The U.S. Environmental Protection Agency (EPA), Office of Research and Development (ORD) conducted a demonstration to evaluate the performance of innovative x-ray fluorescence (XRF) technologies for measuring trace elements in soil and sediment. The demonstration was conducted as part of the EPA Superfund Innovative Technology Evaluation (SITE) Program. Eight field-portable XRF instruments, which were provided and operated by six XRF technology developers, were evaluated as part of the demonstration. Each of these technology developers and their instruments are listed in Table 1-1. The technology developers brought each of these instruments to the demonstration site during the field portion of the demonstration. The instruments were used to analyze a total of 326 prepared soil and sediment samples that contained 13 target elements. The same sample set was analyzed by a fixed laboratory (the reference laboratory) using established EPA reference methods. The results obtained using each XRF instrument in the field were compared with the results obtained by the reference laboratory to assess instrument accuracy. The results of replicate sample analysis were utilized to assess the precision and the detection limits that each XRF instrument could achieve. The results of these evaluations, as well as technical observations and cost information, were then documented in an Innovative Technology Verification Report (ITVR) for each instrument. This ITVR documents EPA's evaluation of the Elvatech Ltd. ElvaX XRF analyzer (distributed by Xcalibur) based on the results of the demonstration. 1.1 Organization of this Report This report is organized to first present general information pertinent to the demonstration. This information is common to all eight ITVRs that were developed from the XRF demonstration. Specifically, this information includes an introduction (Chapter 1), the locations where the field samples were collected (Chapter 2), the field demonstration (Chapter 3), the evaluation design (Chapter 4), and the reference laboratory results (Chapter 5). The second part of this report provides information relevant to the specific instrument that is the subject of this ITVR. This information includes a description of the instrument (Chapter 6), a performance evaluation (Chapter 7), a cost analysis (Chapter 8), and a summary of the demonstration results (Chapter 9). Table 1-1. Participating Technology Developers and Instruments Developer Full Name Elvatech, Ltd. Innov-X Systems NITON Analyzers, A Division of Thermo Electron Corporation Oxford Instruments Analytical, Ltd. Rigaku, Inc. RONTEC AG (acquired by Bruker AXS, 1 1/2005) Distributor in the United States Xcalibur XRF Services Innov-X Systems NITON Analyzers, A Division of Thermo Electron Corporation Oxford Instruments Analytical, Ltd. Rigaku, Inc. RONTEC USA Developer Short Name Xcalibur Innov-X Niton Oxford Rigaku Rontec Instrument Full Name ElvaX XT400 Series XLt 700 Series XLi 700 Series X-Met 3000 TX ED2000 ZSX Mini II PicoTAX Instrument Short Name ElvaX XT400 XLt XLi X-Met ED2000 ZSX Mini II PicoTAX ------- References are provided in Chapter 10. A verification statement for the instrument is provided as Appendix A. Comments from the instrument developer on the demonstration and any exceptions to EPA's evaluation are presented in Appendix B. Appendices C, D, and E contain the data validation summary report for the reference laboratory data and detailed evaluations of instrument versus reference laboratory results. 1.2 Description of the SITE Program Performance verification of innovative environmental technologies is an integral part of EPA's regulatory and research mission. The SITE Program was established by the EPA Office of Solid Waste and Emergency Response and ORD under the Superfund Amendments and Reauthorization Act of 1986. The overall goal of the SITE Program is to conduct performance verification studies and to promote acceptance of innovative technologies that may be used to achieve long-term protection of human health and the environment. The program is designed to meet three primary objectives: (1) identify and remove obstacles to development and commercial use of innovative technologies; (2) demonstrate promising innovative technologies and gather reliable information on performance and cost to support site characterization and cleanup; and (3) maintain an outreach program to operate existing technologies and identify new opportunities for their use. Additional information on the SITE Program is available on the EPA ORD web site (www. epa.gov/ord/SITE). The intent of a SITE demonstration is to obtain representative, high-quality data on the performance and cost of one or more innovative technologies so that potential users can assess a technology's suitability for a specific application. The SITE Program includes the following program elements: Monitoring and Measurement Technology (MMT) Program - Evaluates technologies that sample, detect, monitor, or measure hazardous and toxic substances. These technologies are expected to provide better, faster, or more cost- effective methods for producing real-time data during site characterization and remediation studies than can conventional technologies. Remediation Technology Program - Demonstrates innovative treatment technologies to provide reliable data on performance, cost, and applicability for site cleanups. Technology Transfer Program - Provides and disseminates technical information in the form of updates, brochures, and other publications that promote the SITE Program and the participating technologies. The demonstration of XRF instruments was conducted as part of the MMT Program, which is administered by the Environmental Sciences Division (ESD) of the National Exposure Research Laboratory (NERL) in Las Vegas, Nevada. Additional information on the NERL ESD is available on the EPA web site (www.epa.gov/nerlesdl/). TetraTech EM Inc. (Tetra Tech), an EPA contractor, provided comprehensive technical support to the demonstration. 1.3 Scope of the Demonstration Conventional analytical methods for measuring the concentrations of inorganic elements in soil and sediment are time-consuming and costly. For this reason, field-portable XRF instruments have been proposed as an alternative approach, particularly where rapid and cost-effective assessment of a site is a goal. The use of a field XRF instrument for elemental analysis allows field personnel to quickly assess the extent of contamination by target elements at a site. Furthermore, the near instantaneous data provided by field-portable XRF instruments can be used to quickly identify areas where there may be increased risks and allow development of a more focused and cost-effective sampling strategy for conventional laboratory analysis. EPA-sponsored demonstrations of XRF technologies have been under way for more than a decade. The first SITE MMT demonstration of XRF occurred in 1995, when six instruments were evaluated for their ability to analyze 10 target elements. The results of this demonstration were published in individual reports for each instrument (EPA 1996a, 1996b, 1998a, 1998b, 1998c, and 1998d). In 2003, two XRF instruments were included in a demonstration of field methods for analysis of mercury in soil and sediment. ------- Individual ITVRs were also prepared for each of these two instruments (EPA 2004a, 2004b). Although XRF spectrometry is now considered a mature technology for elemental analysis, field- portable XRF instruments have evolved considerably over the past 10 years, and many of the instruments that were evaluated in the original demonstration are no longer manufactured. Advances in electronics and data processing, coupled with new x-ray tube source technology, have produced substantial improvements in the precision and speed of XRF analysis. The current demonstration of XRF instruments was intended to evaluate these new technologies, with an expanded set of target elements, to provide information to potential users on current state-of-the- art instrumentation and its associated capabilities. During the demonstration, performance data regarding each field-portable XRF instrument were collected through analysis of a sample set that included a broad range of soil/sediment types and target element concentrations. To develop this sample set, soil and sediment samples that contain the target elements of concern were collected in bulk quantities at nine sites from across the U.S. These bulk samples of soil and sediment were homogenized, characterized, and packaged into demonstration samples for the evaluation. Some of the batches of soil and sediment were spiked with selected target elements to ensure that representative concentration ranges were included for all target elements and that the sample design was robust. Replicate samples of the material in each batch were included in the final set of demonstration samples to assess instrument precision and detection limits. The final demonstration sample set therefore included 326 samples. Each developer analyzed all 326 samples during the field demonstration using its XRF instrument and in accordance with its standard operating procedure. The field demonstration was conducted during the week of January 24, 2005, at the Kennedy Athletic, Recreational and Social (KARS) Park, which is part of the Kennedy Space Center on Merritt Island, Florida. Observers were assigned to each XRF instrument during the field demonstration to collect detailed information on the instrument and operating procedures, including sample processing times, for subsequent evaluation. The reference laboratory also analyzed a complete set of the demonstration samples for the target elements using acid digestion and inductively coupled plasma-atomic emission spectrometry (ICP-AES), in accordance with EPA Method 3 05 OB/601 OB, and using cold vapor atomic absorption (CVAA) spectroscopy (for mercury only) in accordance with EPA Method 7471 A. By assuming that the results from the reference laboratory were essentially "true" values, instrument accuracy was assessed by comparing the results obtained using the XRF instrument with the results from the reference laboratory. The data obtained using the XRF instrument were also assessed in other ways, in accordance with the objectives of the demonstration, to provide information on instrument precision, detection limits, and interferences. 1.4 General Description of XRF Technology XRF spectroscopy is an analytical technique that exposes a solid sample to an x-ray source. The x- rays from the source have the appropriate excitation energy that causes elements in the sample to emit characteristic x-rays. A qualitative elemental analysis is possible from the characteristic energy, or wavelength, of the fluorescent x-rays emitted. A quantitative elemental analysis is possible by counting the number (intensity) of x-rays at a given wavelength. Three electron shells are generally involved in emissions of x-rays during XRF analysis of samples: the K, L, and M shells. Multiple-intensity peaks are generated from the K, L, or M shell electrons in a typical emission pattern, also called an emission spectrum, for a given element. Most XRF analysis focuses on the x-ray emissions from the K and L shells because they are the most energetic lines. K lines are typically used for elements with atomic numbers from 11 to 46 (sodium to palladium), and L lines are used for elements above atomic number 47 (silver). M-shell emissions are measurable only for metals with an atomic number greater than 57 (lanthanum). As illustrated in Figure 1-1, characteristic radiation arises when the energy from the x-ray source exceeds ------- Ejected K-shell electron Incident radiation L-shel! electron fills vacancy K3x-ray Emitted M-shell electron nils vacancy Figure 1-1. The XRF process. the absorption edge energy of inner-shell electrons, ejecting one or more electrons. The vacancies are filled by electrons that cascade in from the outer shells. The energy states of the electrons in the outer shells are higher than those of the inner-shell electrons, and the outer-shell electrons emit energy in the form of x-rays as they cascade down. The energy of this x-ray radiation is unique for each element. An XRF analyzer consists of three major components: (1) a source that generates x-rays (a radioisotope or x-ray tube); (2) a detector that converts x-rays emitted from the sample into measurable electronic signals; and (3) a data processing unit that records the emission or fluorescence energy signals and calculates the elemental concentrations in the sample. Measurement times vary (typically ranging from 30 to 600 seconds), based primarily on data quality objectives. Shorter analytical measurement times (30 seconds) are generally used for initial screening, element identification, and hot-spot delineation, while longer measurement times (300 seconds or more) are typically used to meet higher goals for precision and accuracy. The length of the measuring time will also affect the detection limit; generally, the longer the measuring time, the lower the detection limit. However, detection limits for individual elements may be increased because of sample heterogeneity or the presence of other elements in the sample that fluoresce with similar x-ray energies. The main variables that affect precision and accuracy for XRF analysis are: 1. Physical matrix effects (variations in the physical character of the sample). 2. Chemical matrix effects (absorption and enhancement phenomena) and Spectral interferences (peak overlaps). 3. Moisture content above 10 percent, which affects x-ray transmission. Because of these variables, it is important that each field XRF characterization effort be guided by a well- considered sampling and analysis plan. Sample preparation and homogenization, instrument calibration, and laboratory confirmation analysis are all important aspects of an XRF sampling and analysis plan. EPA SW-846 Method 6200 provides additional guidance on sampling and analytical methodology for XRF analysis. 1.5 Properties of the Target Elements This section describes the target elements selected for the technology demonstration and the typical characteristics of each. Key criteria used in selecting the target elements included: The frequency that the element is determined in environmental applications of XRF instruments. The extent that the element poses an environmental consequence, such as a potential risk to human or environmental receptors. The ability of XRF technology to achieve detection limits below typical remediation goals and risk assessment criteria. The extent that the element may interfere with the analysis of other target elements. In considering these criteria, the critical target elements selected for this study were antimony, arsenic, cadmium, chromium, copper, iron, lead, mercury, nickel, selenium, silver, vanadium, and zinc. These 13 target elements are of significant concern for site cleanups and human health risk assessments because most are highly toxic or interfere with the analysis of other elements. The demonstration therefore focused on the analysis of these 13 elements in evaluating the various XRF instruments. ------- 7.5.7 Antimony Naturally occurring antimony in surface soils is typically found at less than 1 to 4 milligrams per kilogram (mg/kg). Antimony is mobile in the environment and is bioavailable for uptake by plants; concentrations greater than 5 mg/kg are potentially phytotoxic; and concentrations above 31 mg/kg in soil may be hazardous to humans. Antimony may be found along with arsenic in mine wastes, at shooting ranges, and at industrial facilities. Typical detection limits for field-portable XRF instruments range from 10 to 40 mg/kg. Antimony is typically analyzed with success by ICP-AES; however, recovery of antimony in soil matrix spikes is often below quality control (QC) limits (50 percent or less) as a result of loss through volatilization during acid digestion. Therefore, results using ICP-AES may be lower than are obtained by XRF. 7.5.2 Arsenic Naturally occurring arsenic in surface soils typically ranges from 1 to 50 mg/kg; concentrations above 10 mg/kg are potentially phytotoxic. Concentrations of arsenic greater than 0.39 mg/kg may cause carcinogenic effects in humans, and concentrations above 22 mg/kg may result in adverse noncarcinogenic effects. Typical detection limits for field-portable XRF instruments range from 10 to 20 mg/kg arsenic. Elevated concentrations of arsenic are associated with mine wastes and industrial facilities. Arsenic is successfully analyzed by ICP-AES; however, spectral interferences between peaks for arsenic and lead can affect detection limits and accuracy in XRF analysis when the ratio of lead to arsenic is 10 to 1 or more. Risk-based screening levels and soil screening levels for arsenic may be lower than the detection limits of field-portable XRF instruments. 7.5.5 Cadmium Naturally occurring cadmium in surface soils typically ranges from 0.6 to 1.1 mg/kg; concentrations greater than 4 mg/kg are potentially phytotoxic. Concentrations of cadmium that exceed 37 mg/kg may result in adverse effects in humans. Typical detection limits for field-portable XRF instruments range from 10 to 50 mg/kg. Elevated concentrations of cadmium are associated with mine wastes and industrial facilities. Cadmium is successfully analyzed by both ICP-AES and field- portable XRF; however, action levels for cadmium may be lower than the detection limits of field- portable XRF instruments. 1.5.4 Chromium Naturally occurring chromium in surface soils typically ranges from 1 to 1,000 mg/kg; concentrations greater than 1 mg/kg are potentially phytotoxic, although specific phytotoxicity levels for naturally occurring chromium have not been documented. The variable oxidation states of chromium affect its behavior and toxicity. Concentrations of hexavalent chromium above 30 mg/kg and of trivalent chromium above 10,000 mg/kg may cause adverse health effects in humans. Typical detection limits for field-portable XRF instruments range from 10 to 50 mg/kg. Hexavalent chromium is typically associated with metal plating or other industrial facilities. Trivalent chromium may be found in mine waste and at industrial facilities. Neither ICP-AES nor field-portable XRF can distinguish between oxidation states for chromium (or any other element). 7.5.5 Copper Naturally occurring copper in surface soils typically ranges from 2 to 100 mg/kg; concentrations greater than 100 mg/kg are potentially phytotoxic. Concentrations greater than 3,100 mg/kg may result in adverse health effects in humans. Typical detection limits for field-portable XRF instruments range from 10 to 50 mg/kg. Copper is mobile and is a common contaminant in soil and sediments. Elevated concentrations of copper are associated with mine wastes and industrial facilities. Copper is successfully analyzed by ICP-AES and XRF; however, spectral interferences between peaks for copper and zinc may affect the detection limits and accuracy of the XRF analysis. 7.5.6 Iron Although iron is not considered an element that poses a significant environmental consequence, it interferes with measurement of other elements and was ------- therefore included in the study. Furthermore, iron is often used as a target reference element in XRF analysis. Naturally occurring iron in surface soils typically ranges from 7,000 to 550,000 mg/kg, with the iron content originating primarily from parent rock. Typical detection limits for field-portable XRF instruments are in the range of 10 to 60 mg/kg. Iron is easily analyzed by both ICP-AES and XRF; however, neither technique can distinguish among iron species in soil. Although iron in soil may pose few environmental consequences, high levels of iron may interfere with analyses of other elements in both techniques (ICP-AES and XRF). Spectral interference from iron is mitigated in ICP-AES analysis by applying inter-element correction factors, as required by the analytical method. Differences in analytical results between ICP-AES and XRF for other target elements are expected when concentrations of iron are high in the soil matrix. 1.5.7 Lead Naturally occurring lead in surface soils typically ranges from 2 to 200 mg/kg; concentrations greater than 50 mg/kg are potentially phytotoxic. Concentrations greater than 400 mg/kg may result in adverse effects in humans. Typical detection limits for field-portable XRF instruments range from 10 to 20 mg/kg. Lead is a common contaminant at many sites, and human and environmental exposure can occur through many routes. Lead is frequently found in mine waste, at lead-acid battery recycling facilities, at oil refineries, and in lead-based paint. Lead is successfully analyzed by ICP-AES and XRF; however, spectral interferences between peaks for lead and arsenic in XRF analysis can affect detection limits and accuracy when the ratio of arsenic to lead is 10 to 1 or more. Differences between ICP-AES and XRF results are expected in the presence of high concentrations of arsenic, especially when the ratio of lead to arsenic is low. 7.5.* Mercury Naturally occurring mercury in surface soils typically ranges from 0.01 to 0.3 mg/kg; concentrations greater than 0.3 mg/kg are potentially phytotoxic. Concentrations of mercury greater than 23 mg/kg and concentrations of methyl mercury above 6.1 mg/kg may result in adverse health effects in humans. Typical detection limits for field-portable XRF instruments range from 10 to 20 mg/kg. Elevated concentrations of mercury are associated with amalgamation of gold and with mine waste and industrial facilities. Native surface soils are commonly enriched by anthropogenic sources of mercury. Anthropogenic sources include coal-fired power plants and metal smelters. Mercury is too volatile to withstand both the vigorous digestion and extreme temperature involved with ICP-AES analysis; therefore, the EPA-approved technique for laboratory analysis of mercury is CVAA spectroscopy. Mercury is successfully measured by XRF, but differences between results obtained by CVAA and XRF are expected when mercury levels are high. 7.5.9 Nickel Naturally occurring nickel in surface soils typically ranges from 5 to 500 mg/kg; a concentration of 30 mg/kg is potentially phytotoxic. Concentrations greater than 1,600 mg/kg may result in adverse health effects in humans. Typical detection limits for field- portable XRF instruments range from 10 to 60 mg/kg. Elevated concentrations of nickel are associated with mine wastes and industrial facilities. Nickel is a common environmental contaminant at metal processing sites. It is successfully analyzed by both ICP-AES and XRF with little interference; therefore, a strong correlation between the methods is expected. 7.5.70 Selenium Naturally occurring selenium in surface soils typically ranges from 0.1 to 2 mg/kg; concentrations greater than 1 mg/kg are potentially phytotoxic. Its toxicities are well documented for plants and livestock; however, it is also considered a trace nutrient. Concentrations above 390 mg/kg may result in adverse health effects in humans. Typical detection limits for field-portable XRF instruments range from 10 to 20 mg/kg. Most selenium is associated with sulfur or sulfide minerals, where concentrations can exceed 200 mg/kg. Selenium can be measured by both ICP-AES and XRF; however, detection limits using XRF usually exceed the ------- ecological risk-based screening levels for soil. Analytical results for selenium using ICP-AES and XRF are expected to be comparable. 7.5.77 Silver Naturally occurring silver in surface soils typically ranges from 0.01 to 5 mg/kg; concentrations greater than 2 mg/kg are potentially phytotoxic. In addition, concentrations that exceed 390 mg/kg may result in adverse effects in humans. Typical detection limits for field-portable XRF instruments range from 10 to 45 mg/kg. Silver is mobile and is a common contaminant in mine waste, in photographic film processing wastes, and at metal processing sites. It is successfully analyzed by ICP-AES and XRF; however, recovery may be reduced in ICP-AES analysis because insoluble silver chloride may form during acid digestion. Detection limits using XRF may exceed the risk-based screening levels for silver in soil. 1.5.12 Van adium Naturally occurring vanadium in surface soils typically ranges from 20 to 500 mg/kg; concentrations greater than 2 mg/kg are potentially phytotoxic, although specific phytotoxicity levels for naturally occurring vanadium have not been documented. Concentrations above 550 mg/kg may result in adverse health effects in humans. Typical detection limits for field-portable XRF instruments range from 10 to 50 mg/kg. Vanadium can be associated with manganese, potassium, and organic matter and is typically concentrated in organic shales, coal, and crude oil. It is successfully analyzed by both ICP-AES and XRF with little interference. 7.5.75 Zinc Naturally occurring zinc in surface soils typically ranges from 10 to 300 mg/kg; concentrations greater than 50 mg/kg are potentially phytotoxic. Zinc at concentrations above 23,000 mg/kg may result in adverse health effects in humans. Typical detection limits for field-portable XRF instruments range from 10 to 30 mg/kg. Zinc is a common contaminant in mine waste and at metal processing sites. In addition, it is highly soluble, which is a common concern for aquatic receptors. Zinc is successfully analyzed by ICP-AES; however, spectral interferences between peaks for copper and zinc may influence detection limits and the accuracy of the XRF analysis. ------- This page was left blank intentionally. ------- Chapter 2 Field Sample Collection Locations Although the field demonstration took place at KARS Park on Merritt Island, Florida, environmental samples were collected at other sites around the country to develop a demonstration sample that incorporated a variety of soil/sediment types and target element concentrations. This chapter describes these sample collection sites, as well as the rationale for the selection of each. Several criteria were used to assess potential sample collection sites, including: The ability to provide a variety of target elements and soil/sediment matrices. The convenience and accessibility of the location to the sampling team. Program support and the cooperation of the site owner. Nine sample collection sites were ultimately selected for the demonstration; one was the KARS Park site itself. These nine sites were selected to represent variable soil textures (sand, silt, and clay) and iron content, two factors that significantly affect instrument performance. Historical operations at these sites included mining, smelting, steel manufacturing, and open burn pits; one, KARS Park, was a gun range. Thus, these sites incorporated a wide variety of metal contaminants in soils and sediments. Both contaminated and uncontaminated (background) samples were collected at each site. A summary of the sample collection sites is presented in Table 2-1, which describes the types of metal- contaminated soils or sediments that were found at each site. This information is based on the historical data that were provided by the site owners or by the EPA remedial project managers. 2.1 Alton Steel Mill Site The Alton Steel Mill site (formerly the Laclede Steel site) is located at 5 Cut Street in Alton, Illinois. This 400-acre site is located in Alton's industrial corridor. The Alton site was operated by Laclede Steel Company from 1911 until it went bankrupt in July 2001. The site was purchased by Alton Steel, Inc., from the bankruptcy estate of Laclede Steel in May 2003. The Alton site is heir to numerous environmental concerns from more than 90 years of steel production; site contaminants include polychlorinated biphenyls (PCBs) and heavy metals. Laclede Steel was cited during its operating years for improper management and disposal of PCB wastes and electric arc furnace dust that contained heavy metals such as lead and cadmium. A Phase I environmental site assessment (ESA) was conducted at the Alton site in May 2002, which identified volatile organic compounds (VOCs), semivolatile organic compounds (SVOCs), total priority pollutant metals, and PCBs as potential contaminants of concern at the site. Based on the data gathered during the Phase I ESA and on discussions with Alton personnel, several soil samples were collected for the demonstration from two areas at the Alton site, including the Rod Patenting Building and the Tube Mill Building. The soil in the areas around these two buildings had not been remediated and was known to contain elevated concentrations of arsenic, cadmium, chromium, lead, nickel, zinc, and iron. The matrix of the contaminated soil samples was a fine to medium sand; the background soil sample was a sand loam. Table 2-2 presents historical analytical data (the maximum concentrations) for some of the target elements detected at the Alton site. ------- Table 2-1. Nature of Contamination in Soil and Sediment at Sample Collection Sites Sample Collection Site Alton Steel, Alton, IL Burlington Northern- ASARCO Smelter Site, East Helena, MT KARS Park - Kennedy Space Center, Merritt Island, FL Leviathan Mine Site/ Aspen Creek, Alpine County, CA Naval Surface Warfare Center, Crane Division, Crane, IN Ramsay Flats-Silver Bow Creek, Butte, MT Sulphur Bank Mercury Mine Torch Lake Site (Great Lakes Area of Concern), Houghton County, MI Wickes Smelter Site, Jefferson City, MT Source of Contamination Steel manufacturing facility with metal arc furnace dust. The site also includes a metal scrap yard and a slag recovery facility. Railroad yard staging area for smelter ores. Contaminated soils resulted from dumping and spilling concentrated ores. Impacts to soil from historical facility operations and a former gun range. Abandoned open-pit sulfur and copper mine that has contaminated a 9-mile stretch of mountain creeks, including Aspen Creek, with heavy metals. Open disposal and burning of general refuse and waste associated with aircraft maintenance. Silver Bow Creek was used as a conduit for mining, smelting, industrial, and municipal wastes. Inactive mercury mine. Waste rock, tailings, and ore are distributed in piles throughout the property. Copper mining produced mill tailings that were dumped directly into Torch Lake, contaminating the lake sediments and shoreline. Abandoned smelter complex with contaminated soils and mineral-processing wastes, including remnant ore piles, decomposed roaster brick, slag piles and fines, and amalgamation sediments. Matrix Soil Soil Soil Soil and Sediment Soil Soil and Sediment Soil Sediment Soil Site-Specific Metals of Concern for XRF Demonstration Sb X X X X As X X X X X X X X X Cd X X X X X X Cr X X X X X X Cu X X X X X X Fe X X X X X Pb X X X X X X X X Hg X X X Ni X X X X Se X Aฃ X X Zn X X X X X X Notes (in order of appearance in table): Sb: Antimony Cr: Chromium Pb: Lead As: Arsenic Cu: Copper Hg: Mercury Cd: Cadmium Fe: Iron Ni: Nickel Note: Vanadium was not a chemical of concern at any of the sites and so does not appear on the table. Se: Selenium Ag: Silver Zn: Zinc 10 ------- Table 2-2. Historical Analytical Data, Alton Steel Mill Site 2.3 Kennedy Athletic, Recreational and Social Park Site Metal Arsenic Cadmium Chromium Lead Maximum Concentration (mg/kg) 80.3 97 1,551 3,556 2.2 Burlington Northern-ASARCO Smelter Site The Burlington Northern (BN)-ASARCO Smelter site is located in the southwestern part of East Helena, Montana. The site was an active smelter for more than 100 years and closed in 2002. Most of the ore processed at the smelter was delivered on railroad cars. An area west of the plant site (the BN property) was used for temporary staging of ore cars and consists of numerous side tracks to the primary railroad line into the smelter. This site was selected to be included in the demonstration because it had not been remediated and contained several target elements in soil. At the request of EPA, the site owner collected samples of surface soil in this area in November 1997 and April 1998 and analyzed them for arsenic, cadmium, and lead; elevated concentrations were reported for all three metals. The site owner collected 24 samples of surface soil (16 in November 1997 and 8 in April 1998). The soils were found to contain up to 2,018 parts per million (ppm) arsenic, 876 ppm cadmium, and 43,907 ppm lead. One sample of contaminated soil and one sample of background soil were collected. The contaminated soil was a light brown sandy loam with low organic carbon content. The background soil was a medium brown sandy loam with slightly more organic material than the contaminated soil sample. Table 2- 3 presents the site owner's data for arsenic, cadmium, and lead (the maximum concentrations) from the 1997 and 1998 sampling events. Table 2-3. Historical Analytical Data, BN- ASARCO Smelter Site Soil and sediment at the KARS Park site were contaminated from former gun range operations and contain several target elements for the demonstration. The specific elements of concern for the KARS Park site include antimony, arsenic, chromium, copper, lead, and zinc. The KARS Park site is located at the Kennedy Space Center on Merritt Island, Florida. KARS Park was purchased in 1962 and has been used by employees of the National Aeronautics and Space Administration (NASA), other civil servants, and guests as a recreational park since 1963. KARS Park occupies an area of Kennedy Space Center just outside the Cape Canaveral base. Contaminants in the park resulted from historical facility operations and impacts from the former gun range. The land north of KARS is owned by NASA and is managed by the U.S. Fish and Wildlife Service (USFWS) as part of the Merritt Island National Wildlife Refuge. Two soil and two sediment samples were collected from various locations at the KARS Park site for the XRF demonstration. The contaminated soil sample was collected from an impact berm at the small arms range. The background soil sample was collected from a forested area near the gun range. The matrix of the contaminated and background soil samples consisted of fine to medium quartz sand. The sediment samples were collected from intermittently saturated areas within the skeet range. These samples were organic rich sandy loams. Table 2-4 presents historical analytical data (the maximum concentrations) for soil and sediment at KARS Park. Table 2-4. Historical Analytical Data, KARS Park Site Metal Arsenic Cadmium Lead Maximum Concentration (ppm) 2,018 876 43,907 Metal Antimony Arsenic Chromium Copper Lead Zinc Maximum Concentration (mg/kg) 8,500 1,600 40.2 290,000 99,000 16,200 11 ------- 2.4 Leviathan Mine Site The Leviathan Mine site is an abandoned copper and sulfur mine located high on the eastern slopes of the Sierra Nevada Mountain range near the California- Nevada border. Development of the Leviathan Mine began in 1863, when copper sulfate was mined for use in the silver refineries of the Comstock Lode. Later, the underground mine was operated as a copper mine until a mass of sulfur was encountered. Mining stopped until about 1935, when sulfur was extracted for use in refining copper ore. In the 1950s, the mine was converted to an open-pit sulfur mine. Placement of excavated overburden and waste rock in nearby streams created acid mine drainage and environmental impacts in the 1950s. Environmental impacts noted at that time included large fish kills. Historical mining distributed waste rock around the mine site and created an open pit, adits, and solution cavities through mineralized rock. Oxygen in contact with the waste rock and mineralized rock in the adits oxidizes sulfur and sulfide minerals, generating acid. Water contacting the waste rock and flowing through the mineralized rock mobilizes the acid into the environment. The acid dissolves metals, including arsenic, copper, iron, and nickel, which creates conditions toxic to insects and fish in Leviathan, Aspen, and Bryant Creeks, downstream of the Leviathan Mine. Table 2-5 presents historical analytical data (the maximum concentrations) for the target elements detected at elevated concentrations in sediment samples collected along the three creeks. Four sediment and one soil sample were collected. One of the sediment samples was collected from the iron precipitate terraces formed from the acid mine drainage. The matrix of this sample appeared to be an orange silty clay loam. A second sediment sample was collected from the settling pond at the wastewater treatment system. The matrix of this sample was orange clay. A third sample was collected from the salt crust at the settling pond. This sample incorporated white crystalline material. One background sediment and one background soil sample were collected upstream of the mine. These samples consisted of light brown sandy loam. Table 2-5. Historical Analytical Data, Leviathan Mine Site Metal Arsenic Cadmium Chromium Copper Nickel Maximum Concentration (mg/kg) 2,510 25.7 279 837 2,670 2.5 Navy Surface Warfare Center, Crane Division Site The Old Burn Pit at the Naval Surface Warfare Center (NSWC), Crane Division, was selected to be included in the demonstration because 6 of the 13 target elements were detected at significant concentration in samples of surface soil previously collected at the site. The NSWC, Crane Division, site is located near the City of Crane in south-central Indiana. The Old Burn Pit is located in the northwestern portion of NSWC and was used daily from 1942 to 1971 to burn refuse. Residue from the pit was buried along with noncombustible metallic items in a gully north of the pit. The burn pit was covered with gravel and currently serves as a parking lot for delivery trailers. The gully north of the former burn pit has been revegetated. Several soil samples were collected from the revegetated area for the demonstration because the highest concentrations of the target elements were detected in soil samples collected previously from this area. The matrix of the contaminated and background soil samples was a sandy loam. The maximum concentrations of the target elements detected in surface soil during previous investigations are summarized in Table 2-6. 12 ------- Table 2-6. Historical Analytical Data, NSWC Crane Division-Old Burn Pit Metal Antimony Arsenic Cadmium Chromium Copper Iron Lead Mercury Nickel Silver Zinc Maximum Concentration (mg/kg) 301 26.8 31.1 112 1,520 105,000 16,900 0.43 62.6 7.5 5,110 2.6 Ramsay Flats-Silver Bow Creek Site The Ramsay Flats-Silver Bow Creek site was selected to be included in the demonstration because 6 of the 13 target elements were detected in samples of surface sediment collected previously at the site. Silver Bow Creek originates north of Butte, Montana, and is a tributary to the upper Clark Fork River. More than 100 years of nearly continuous mining have altered the natural environment surrounding the upper Clark Fork River. Early wastes from mining, milling, and smelting were dumped directly into Silver Bow Creek and were subsequently transported downstream. EPA listed Silver Bow Creek and a contiguous portion of the upper Clark Fork River as a Superfund site in 1983. A large volume of tailings was deposited in a low- gradient reach of Silver Bow Creek in the Ramsay Flats area. Tailings at Ramsay Flats extend several hundred feet north of the Silver Bow Creek channel. About 18 inches of silty tailings overlie texturally stratified natural sediments that consist of low- permeability silt, silty clay, organic layers, and stringers of fine sand. Two sediment samples were collected from the Ramsay Flats tailings area and were analyzed for a suite of metals using a field-portable XRF. The contaminated sediment sample was collected in Silver Bow Creek adjacent to the mine tailings. The matrix of this sediment sample was orange-brown silty fine sand with interlayered black organic material. The background sediment sample was collected upstream of Butte, Montana. The matrix of this sample was organic rich clayey silt with approximately 25 percent fine sand. The maximum concentrations of the target elements in the samples are summarized in Table 2-7. Table 2-7. Historical Analytical Data, Ramsay Flats-Silver Bow Creek Site Metal Arsenic Cadmium Copper Iron Lead Zinc Maximum Concentration (mg/kg) 176 141 1,110 20,891 394 1,459 2.7 Sulphur Bank Mercury Mine Site The Sulphur Bank Mercury Mine (SBMM) is a 160- acre inactive mercury mine located on the eastern shore of the Oaks Arm of Clear Lake in Lake County, California, 100 miles north of San Francisco. Between 1864 and 1957, SBMM was the site of underground and open-pit mining at the hydrothermal vents and hot springs. Mining disturbed about 160 acres of land at SBMM and generated large quantities of waste rock (rock that did not contain economic concentrations of mercury and was removed to gain access to ore), tailings (the waste material from processes that removed the mercury from ore), and ore (rock that contained economic concentrations of mercury that was mined and stockpiled for mercury extraction). The waste rock, tailings, and ore are distributed in piles throughout the property. Table 2-8 presents historical analytical data (the maximum concentrations) for the target elements detected at elevated concentrations in surface samples collected at SBMM. Two contaminated soil samples and one background soil sample were collected at various locations for the demonstration project. The mercury sample was collected from the ore stockpile and consisted of medium to coarse sand. The second contaminated soil sample was collected from the waste rock pile and consisted of coarse sand 13 ------- and gravel with trace silt. The matrix of the background soil sample was brown sandy loam. Table 2-8. Historical Analytical Data, Sulphur Bank Mercury Mine Site Table 2-9. Historical Analytical Data, Torch Lake Superfund Site Metal Antimony Arsenic Lead Mercury Maximum Concentration (mg/kg) 3,724 532 900 4,296 2.8 Torch Lake Superfund Site The Torch Lake Superfund site was selected because native and contaminated sediment from copper mining, milling, and smelting contained the elements targeted for the demonstration. The specific metals of concern for the Torch Lake Superfund site included arsenic, chromium, copper, lead, mercury, selenium, silver, and zinc. The Torch Lake Superfund site is located on the Keweenaw Peninsula in Houghton County, Michigan. Wastes were generated at the site from the 1890s until 1969. The site was included on the National Priorities List in June 1986. Approximately 200 million tons of mining wastes were dumped into Torch Lake and reportedly filled about 20 percent of the lake's original volume. Contaminated sediments are believed to be up to 70 feet thick in some locations. Wastes occur both on the uplands and in the lake and are found in four forms, including poor rock piles, slag and slag-enriched sediments, stamp sands, and abandoned settling ponds for mine slurry. EPA initiated long-term monitoring of Torch Lake in 1999; the first monitoring event (the baseline study) was completed in August 2001. Table 2-9 presents analytical data (the maximum concentrations) for eight target elements in sediment samples collected from Torch Lake during the baseline study. Sediment samples were collected from the Torch Lake site at various locations for the demonstration. The matrix of the sediment samples was orange silt and clay. Metal Arsenic Chromium Copper Lead Mercury Selenium Silver Zinc Maximum Concentration'(mg/kg) 40 90 5,850 325 1.2 0.7 6.2 630 2.9 Wickes Smelter Site The roaster slag pile at the Wickes Smelter site was selected to be included in the demonstration because 12 of the 13 target elements were detected in soil samples collected previously at the site. The Wickes Smelter site is located in the unincorporated town of Wickes in Jefferson County, Montana. Wastes at the Wickes Smelter site include waste rock, slag, flue bricks, and amalgamation waste. The wastes are found in discrete piles and are mixed with soil. The contaminated soil sample was collected from a pile of roaster slag at the site. The slag was black, medium to coarse sand and gravel. The matrix of the background soil sample was a light brown sandy loam. Table 2-10 presents historical analytical data (maximum concentrations) for the roaster slag pile. Table 2-10. Historical Analytical Data, Wickes Smelter Site-Roaster Slag Pile Metal Antimony Arsenic Cadmium Chromium Copper Iron Lead Nickel Silver Zinc Maximum Concentration (mg/kg) 79 3,182 70 13 948 24,780 33,500 7.3 83 5,299 14 ------- Chapter 3 Field Demonstration The field demonstration required a sample set and a single location (the demonstration site) where all the technology developers could assemble to analyze the sample set under the oversight of the EPA/Tetra Tech field team. This chapter describes how the sample set was created, how the demonstration site was selected, and how the field demonstration was conducted. Additional detail regarding these topics is available in the Demonstration and Quality Assurance Project Plan (Tetra Tech 2005). 3.1 Bulk Sample Processing A set of samples that incorporated a variety of soil and sediment types and target element concentrations was needed to conduct a robust evaluation. The demonstration sample set was generated from the bulk soil and sediment samples that were collected from the nine sample collection sites described in Chapter 2. Both contaminated (environmental) and uncontaminated (background) bulk samples of soil and sediment were collected at each sample collection site. The background sample was used as source material for a spiked sample when the contaminated sample did not contain the required levels of target elements. By incorporating a spiked background sample into the sample set, the general characteristics of the soil and sediment sample matrix could be maintained. At the same time, this spiked sample assured that all target elements were present at the highest concentration levels needed for a robust evaluation. 3.1.1 Bulk Sample Collection and Shipping Large quantities of soil and sediment were needed for processing into well-characterized samples for this demonstration. As a result, 14 soil samples and 11 sediment samples were collected in bulk quantity from the nine sample collection sites across the U.S. A total of approximately 1,500 kilograms of unprocessed soil and sediment was collected, which yielded more than 1,000 kilograms of soil and sediment after the bulk samples had been dried. Each bulk soil sample was excavated using clean shovels and trowels and then placed into clean, plastic 5-gallon (19-liter) buckets at the sample collection site. The mass of soil and sediment in each bucket varied, but averaged about 25 kilograms per bucket. As a result, multiple buckets were needed to contain the entire quantity of each bulk sample. Once it had been filled, a plastic lid was placed on each bucket, the lid was secured with tape, and the bucket was labeled with a unique bulk sample number. Sediment samples were collected in a similar method at all sites except at Torch Lake, where sediments were collected using a Vibracore or Ponar sediment sampler operated from a boat. Each 5-gallon bucket was overpacked in a plastic cooler and was shipped under chain of custody via overnight delivery to the characterization laboratory, Applied Research and Development Laboratory (ARDL). 3.1.2 Bulk Sample Preparation and Homogenization Each bulk soil or sediment sample was removed from the multiple shipping buckets and then mixed and homogenized to create a uniform batch. Each bulk sample was then spread on a large tray at ARDL's laboratory to promote uniform air drying. Some bulk samples of sediment required more than 2 weeks to dry because of the high moisture content. The air-dried bulk samples of soil and sediment were sieved through a custom-made screen to remove coarse material larger than about 1 inch. Next, each bulk sample was mechanically crushed using a hardened stainless-steel hammer mill until the particle size was sub-60-mesh sieve (less than 0.2 millimeters). The particle size of the processed bulk soil and sediment was measured after each round of crushing using standard sieve technology, and the particles that were still larger than 60-mesh were returned to the crushing process. The duration of the crushing process for each bulk sample varied based on soil type and volume of coarse fragments. 15 ------- After each bulk sample had been sieved and crushed, the sample was mixed and homogenized using a Model T 50A Turbula shaker-mixer. This shaker was capable of handling up to 50 gallons (190 liters) of sample material; thus, this shaker could handle the complete volume of each bulk sample. Bulk samples of smaller volume were mixed and homogenized using a Model T 10B Turbula shaker-mixer that was capable of handling up to 10 gallons (38 liters). Aliquots from each homogenized bulk sample were then sampled and analyzed in triplicate for the 13 target elements using ICP-AES and CVAA. If the relative percent difference between the highest and lowest result exceeded 10 percent for any element, the entire batch was returned to the shaker-mixer for additional homogenization. The entire processing scheme for the bulk samples is shown in Figure 3-1. Yes- Was the material smaller than .2mm? the sample greater than 10 gallons? Material was sieved through custom 1" screen to remove large material. Material crushed using * Samples are mixed and homogenized using Model T 50A Turbula shaker-mixer Samples are mixed and homogenized using Model T 10B and Turbula shaker-mixer Material crushed using stainless steel hammer mill A k Aliquots from each homogenized soil and sediment batch were sampled and analyzed in triplicate using ICP-AES and CVAA for the target elements Was the percent difference between the highest and lowest result greater than 10%? Package samples tor distribution Figure 3-1. Bulk sample processing diagram. 16 ------- 3.2 Demonstration Samples 3.2.2 Spiked Samples After the bulk soil and sediment sample material had been processed into homogenized bulk samples for the demonstration, the next consideration was the concentrations of target elements. The goal was to create a demonstration sample set that would cover the concentration range of each target element that may be reasonably found in the environment. Three concentration levels were identified as a basis for assessing both the coverage of the environmental samples and the need to generate spiked samples. These three levels were: (1) near the detection limit, (2) at intermediate concentrations, and (3) at high concentrations. A fourth concentration level (very high) was added for lead, iron, and zinc in soil and for iron in sediment. Table 3-1 lists the numerical ranges of the target elements for each of these levels (1 through 4). 3.2.1 Environmental Samples A total of 25 separate environmental samples were collected from the nine sample collection sites described in Chapter 2. This bulk environmental sample set included 14 soil and 11 sediment samples. The concentrations of the target elements in some of these samples, however, were too high or too low to be used for the demonstration. Therefore, the initial analytical results for each bulk sample were used to establish different sample blends for each sampling location that would better cover the desired concentration ranges. The 14 bulk soil samples were used to create 26 separate sample blends and the 11 bulk sediment samples were used to create 19 separate sample blends. Thus, there were 45 environmental sample blends in the final demonstration sample set. Either five or seven replicate samples of each sample blend were included in the sample set for analysis during the demonstration. Table 3-2 lists the number of sample blends and the number of demonstration samples (including replicates) that were derived from the bulk environmental samples for each sampling location. Spiked samples that incorporated a soil and sediment matrix native to the sampling locations were created by adding known concentrations of target elements to the background samples. The spiked concentrations were selected to ensure that a minimum of three samples was available for all concentration levels for each target element. After initial characterization at ARDL's laboratory, all bulk background soil and sediment samples were shipped to Environmental Research Associates (ERA) to create the spiked samples. The spiked elements were applied to the bulk sample in an aqueous solution, and then each bulk spiked sample was blended for uniformity and dried before it was repackaged in sample bottles. Six bulk background soil samples were used at ERA's laboratory to create 12 separate spiked sample blends, and four bulk sediment samples were used to create 13 separate spiked sample blends. Thus, a total of 10 bulk background samples were used to create 25 spiked sample blends. Three or seven replicate samples of each spiked sample blend were included in the demonstration sample set. Table 3-3 lists the number of sample blends and the number of demonstration samples (including replicates) that were derived from the bulk background samples for each sampling location. 3.2.3 Demonstration Sample Set In total, 70 separate blends of environmental and spiked samples were created and a set of 326 samples was developed for the demonstration by including three, five, or seven replicates of each blend in the final demonstration sample set. Thirteen sets of the demonstration samples, consisting of 326 individual samples in 250-milliliter clean plastic sample bottles, were prepared for shipment to the demonstration site and reference laboratory. 17 ------- Table 3-1. Concentration Levels for Target Elements in Soil and Sediment Analyte Level 1 Target Range (mg/kg) Level 2 Target Range (mg/kg) Level 3 Target Range (mg/kg) Level 4 Target Range (mg/kg) SOIL Antimony Arsenic Cadmium Chromium Copper Iron Lead Mercury Nickel Selenium Silver Vanadium Zinc 40 - 400 20 - 400 50-500 50-500 50-500 60 - 5,000 20-1,000 20 - 200 50-250 20-100 45-90 50-100 30-1,000 400 - 2,000 400 - 2,000 500-2,500 500-2,500 500-2,500 5,000-25,000 1,000-2,000 200- 1,000 250-1,000 100-200 90-180 100-200 1,000-3,500 >2,000 >2,000 >2,500 >2,500 >2,500 25,000 - 40,000 2,000- 10,000 >1,000 >1,000 >200 >180 >200 3,500 - 8,000 >40,000 >10,000 >8,000 SEDIMENT Antimony Arsenic Cadmium Chromium Copper Iron Lead Mercury Nickel Selenium Silver Vanadium Zinc 40-250 20 - 250 50-250 50-250 50-500 60 - 5,000 20-500 20 - 200 50-200 20-100 45-90 50-100 30-500 250-750 250-750 250-750 250-750 500- 1,500 5,000-25,000 500- 1,500 200 - 500 200-500 100-200 90-180 100-200 500- 1,500 >750 >750 >750 >750 >1,500 25,000 - 40,000 >1,500 >500 >500 >200 >180 >200 >1,500 >40,000 18 ------- Table 3-2. Number of Environmental Sample Blends and Demonstration Samples Sampling Location Alton Steel Mill Site Burlington Northern-ASARCO East Helena Site Kennedy Athletic, Recreational and Social Park Site Leviathan Mine Site Naval Surface Warfare Center, Crane Division Site Ramsay Flats Silver Bow Creek Superfund Site Sulphur Bank Mercury Mine Site Torch Lake Superfund Site Wickes Smelter Site TOTAL * Number of Sample Blends 2 5 6 7 1 7 9 3 5 45 Number of Demonstration Samples 10 29 32 37 5 37 47 19 31 247 Note: The totals in this table add to those for the spiked blends and replicates as summarized in Table 3-3 to bring the total number of blends to 70 and the total number of samples to 326 for the demonstration. Table 3-3. Number of Spiked Sample Blends and Demonstration Samples Sampling Location Alton Steel Mill Site Burlington Northern-ASARCO East Helena Site Leviathan Mine Site Naval Surface Warfare Center, Crane Division Site Ramsey Flats Silver Bow Creek Superfund Site Sulphur Bank Mercury Mine Site Torch Lake Superfund Site Wickes Smelter Site TOTAL * Number of Spiked Sample Blends 1 2 5 2 6 3 4 2 25 Number of Demonstration Samples 3 6 15 6 22 9 12 6 79 * Note: The totals in this table add to those for the unspiked blends and replicates as summarized in Table 3-2 to bring the total number of blends to 70 and the total number of samples to 326 for the demonstration. 19 ------- 3.3 Demonstration Site and Logistics The field demonstration occurred during the week of January 24, 2005. This section describes the selection of the demonstration site and the logistics of the field demonstration, including sample management. 3.3.1 Demonstration Site Selection The demonstration site was selected from among the list of sample collection sites to simulate a likely field deployment. The following criteria were used to assess which of the nine sample collection sites might best serve as the demonstration site: Convenience and accessibility to participants in the demonstration. Ease of access to the site, with a reasonably sized airport that can accommodate the travel schedules for the participants. Program support and cooperation of the site owner. Sufficient space and power to support developer testing. Adequate conference room space to support a visitors day. A temperate climate so that the demonstration could occur on schedule in January. After an extensive search for candidates, the site selected for the field demonstration was KARS Park, which is part of the Kennedy Space Center on Merritt Island, Florida. KARS Park was selected as the demonstration site for the following reasons: Access and Site Owner Support Represen- atives from NASA were willing to support the field demonstration by providing access to the site, assisting in logistical support during the demonstration, and hosting a visitors day. Facilities Requirements and Feasibility The recreation building was available and was of sufficient size to accommodate all the demonstration participants. Furthermore, the recreation building had adequate power to operate all the XRF instruments simultaneously and all the amenities to fully support the demonstration participants, as well as visitors, in reasonable comfort. Ease of Access to the Site The park, located about 45 minutes away from Orlando International Airport, was selected because of its easy accessibility by direct flight from many airports in the country. In addition, many hotels are located within 10 minutes of the site along the coast at Cocoa Beach, in a popular tourist area. Weather in this area of central Florida in January is dry and sunny, with pleasant daytime temperatures into the 70s (F) and cool nights. 3.3.2 Demonstration Site Logistics The field demonstration was held in the recreation building, which is just south of the gunnery range at KARS Park. Photographs of the KARS Park recreation building, where all the XRF instruments were set up and operated, are shown in Figures 3-2 and 3-3. A visitors day was held on January 26, 2005 when about 25 guests came to the site to hear about the demonstration and to observe the XRF instruments in operation. Visitors day presentations were conducted in a conference building adjacent to the recreation building at KARS Park (see Figure 3-4). Presenta- tions by NASA and EPA representatives were followed by a tour of the XRF instruments in the recreation building while demonstration samples were being analyzed. Figure 3-2. KARS Park recreation building. 20 ------- Figure 3-3. Work areas for the XRF instruments in the recreation building. Figure 3-4. Visitors day presentation. 3.3.3 EPA Demonstration Team and Developer Field Team Responsibilities Each technology developer sent its instrument and a field team to the demonstration site for the week of January 24, 2005. The developer's field team was responsible for unpacking, setting up, calibrating, and operating the instrument. The developer's field team was also responsible for any sample preparation for analysis using the XRF instrument. The EPA/Tetra Tech demonstration team assigned an observer to each instrument. The observer sat beside the developer's field team, or was nearby, throughout the field demonstration and observed all activities involved in setup and operation of the instrument. The observer's specific responsibilities included: Guiding the developer's field team to the work area in the recreation building at KARS Park and assisting with any logistical issues involved in instrument shipping, unpacking, and setup. Providing the demonstration sample set to the developer's field team in accordance with the sample management plan. Ensuring that the developer was operating the instrument in accordance with standard procedures and questioning any unusual practices or procedures. Communications with the developer's field team regarding schedules and fulfilling the requirements of the demonstration. Recording information relating to the secondary objectives of the evaluation (see Chapter 4) and for obtaining any cost information that could be provided by the developer's field team. Receiving the data reported by the developer's field team for the demonstration samples, and loading these data into a temporary database on a laptop computer. Overall, the observer was responsible for assisting the developer's field team throughout the field demonstration and for recording all pertinent information and data for the evaluation. However, the observer was not allowed to advise the developer's field team on sample processing or to provide any feedback based on preliminary inspection of the XRF instrument data set. 3.3.4 Sample Management during the Field Demonstration The developer's field team analyzed the demonstration sample set with its XRF instrument during the field demonstration. Each demonstration sample set was shipped to the demonstration site with only a reference number on each bottle as an identifier. The reference number was tied to the source information in the EPA/Tetra Tech database, but no information was provided on the sample label 21 ------- that might provide the developer's field team any insight as to the nature or content of the sample. Spiked samples were integrated with the environmental samples in a random manner so that the spiked samples could not be distinguished. The demonstration sample set was divided into 13 subsets, or batches, for tracking during the field demonstration. The samples provided to each developer's field team were randomly distributed in two fashions. First, the order of the jars within each batch was random, so that the sample order for a batch was different for each developer's field team. Second, the distribution of sample batches was random, so that each developer's field team received the sample batches in a different order. The observer provided the developer's field team with one batch of samples at a time. When the developer's field team reported that analysis of a batch was complete, the observer would reclaim all the unused sample material from that batch and then provide the next batch of samples for analysis. Chain-of-custody forms were used to document all sample transfers. When the analysis of all batches was complete, the observer assisted the developer's field team in cleanup of the work area and repackaging the instrument and any associated equipment. The members of the developer's field team were not allowed to take any part of the demonstration samples with them when they left the demonstration site. Samples that were not in the possession of the developer's field team during the demonstration were held in a secure storage room adjacent to the demonstration work area (see Figure 3-5). The storage room was closed and locked except when the observer retrieved samples from the room. Samples were stored at room temperature during the demonstration, in accordance with the quality assurance/quality control (QA/QC) requirements established for the project. Figure 3-5. Sample storage room. 3.3.5 Data Man agement Each of the developer's field teams was able to complete analysis of all 326 samples during the field demonstration (or during the subsequent week, in one case when the developer's field team arrived late at the demonstration site because of delays in international travel). The data produced by each developer's field team were submitted during or at the end of the field demonstration in a standard Microsoft Excelฎ spreadsheet. (The EPA/Tetra Tech field team had provided a template.) Since each instrument provided data in a different format, the developer's field team was responsible for reducing the data before they were submitted and for transferring the data into the Excel spreadsheet. The observer reviewed each data submittal for completeness, and the data were then uploaded into a master Excel spreadsheet on a laptop computer for temporary storage. Only the EPA/Tetra Tech field team had access to the master Excel spreadsheet during the field demonstration. Once the EPA/Tetra Tech field team returned to their offices, the demonstration data were transferred to an Microsoft Accessฎ database for permanent storage. Each developer's data, as they existed in the Access database, were then provided to the developer for review. Any errors the developers identified were corrected, and the database was then finalized. All statistical analysis and data evaluation took place on this final database. 22 ------- Chapter 4 Evaluation Design This chapter presents the approach for evaluating the performance of the XRF instruments. Specifically, the sections below describe the objectives of the evaluation and the experimental design. The Demonstration and Quality Assurance Project Plan (Tetra Tech 2005) provides additional details on the overall demonstration approach. However, some deviations from the plan, involving data evaluation and laboratory audits, occurred after the demonstration plan was written. For completeness, the primary changes to the written plan are documented in the final section of this chapter. 4.1 Evaluation Objectives The overall purpose of the XRF technology demonstration was to evaluate the performance of various field XRF instruments in detecting and quantifying trace elements in soils and sediments from a variety of sites around the U.S. The performance of each XRF instrument was evaluated in accordance with primary and secondary objectives. Primary objectives are critical to the evaluation and require the use of quantitative results to draw conclusions about an instrument's performance. Secondary objectives pertain to information that is useful but that will not necessarily require use of quantitative results to draw conclusions about an instrument's performance. The primary and secondary objectives for the evaluation are listed in Table 4-1. These objectives were based on: Input from MMT Program stakeholders, including developers and EPA staff. General expectations of users of field measurement instruments. The time available to complete the demonstration. The capabilities of the instruments that the developers participating in the demonstration intended to highlight. 4.2 Experimental Design To address the first four primary objectives, each XRF instrument analyzed the demonstration sample set for the 13 target elements. The demonstration samples originated from multiple sampling locations across the country, as described in Chapter 2, to provide a diverse set of soil and sediment matrices. The demonstration sample set included both blended environmental samples and spiked background samples, as described in Chapter 3, to provide a wide range of concentrations and combinations of elements. When the field demonstration was completed, the results obtained using the XRF instruments were compared with data from a reference laboratory to evaluate the performance of each instrument in terms of accuracy and comparability (Primary Objective 2). The results for replicate samples were used to evaluate precision in various concentration ranges (Primary Objective 3) and the method detection limits (MDL) (Primary Objective 1). Each of these quantitative evaluations of instrument performance was carried out for each target element. The effect of chemical and spectral interferences and of soil characteristics (Primary Objectives 4 and 5) were evaluated to help explain extreme deviations or outliers observed in the XRF results when compared with the reference laboratory results. A second important comparison involved the average performance of all eight XRF instruments that participated in the demonstration. For the first three primary objectives (MDL, accuracy, precision), the performance of each individual instrument was compared to the overall average performance of all eight instruments. Where the result of the instrument under consideration was less than 10 percent different than the average result for all eight instruments, the result was considered "equivalent." A similar comparison was conducted with respect to cost (Primary Objective 7). These comparisons were intended to illustrate the performance of each XRF instrument in relation to its peers. 23 ------- The evaluation design for meeting each objective, including data analysis procedures, is discussed in more detail in the sections below. Where specific deviations from these procedures were necessary for the data set associated with specific instruments, these deviations are described as part of the performance evaluation in Chapter 7. 4.2.1 Primary Objective 1 Meth od Detection Limits The MDL for each target element was evaluated based on the analysis of sets of seven replicate samples that contained the target element at concentrations near the detection limit. The MDL was calculated using the procedures found in Title 40 Code of Federal Regulations (CFR) Part 136, Appendix B, Revision 1.11. The following equation was used: where MDL = t(n-U-a=0.99)(s) MDL = method detection limit t = Student's t value for a 99 percent confidence level and a standard deviation estimate with n-1 degrees of freedom n = number of samples s = standard deviation. Table 4-1. Evaluation Objectives Objective Primary Objective 1 Primary Objective 2 Primary Objective 3 Primary Objective 4 Primary Objective 5 Primary Objective 6 Primary Objective 7 Secondary Objective 1 Secondary Objective 2 Secondary Objective 3 Secondary Objective 4 Secondary Objective 5 Description Determine the MDL for each target element. Evaluate the accuracy and comparability of the XRF measurement to the results of laboratory reference methods for a variety of contaminated soil and sediment samples. Evaluate the precision of XRF measurements for a variety of contaminated soil and sediment samples. Evaluate the effect of chemical and spectral interference on measurement of target elements. Evaluate the effect of soil characteristics on measurement of target elements. Measure sample throughput for the measurement of target elements under field conditions. Estimate the costs associated with XRF field measurements. Document the skills and training required to properly operate the instrument. Document health and safety concerns associated with operating the instrument. Document the portability of the instrument. Evaluate the instrument's durability based on its materials of construction and engineering design. Document the availability of the instrument and of associated customer technical support. 24 ------- Based on the data provided by the characterization laboratory before the demonstration, a total of 12 sample blends (seven for soil and five for sediment) were identified for use in the MDL determination. The demonstration approach specified the analysis of seven replicates for each of these sample blends by both the developer and the reference laboratory. It was predicted that these blends would allow the determination of a minimum of one MDL for soil and one MDL for sediment for each element, with the exception of iron. This prediction was based on the number of sample blends that contained concentrations less than 50 percent lower or higher than the lower limit of the Level 1 concentration range (from 20 to 50 ppm, depending on the element), as presented in Table 3-1. After the field demonstration, the data sets obtained by the developers and the reference laboratory for the MDL sample blends were reviewed to confirm that they were appropriate to use in calculating MDLs. The requirements of 40 CFR 136, Appendix B, were used as the basis for this evaluation. Specifically, the CFR states that samples to be used for MDL determinations should contain concentrations in the range of 1 to 5 times the predicted MDL. On this basis, and using a nominal predicted reporting limit of 50 ppm for the target elements based on past XRF performance and developer information, a concentration of 250 ppm (5 times the "predicted" nominal MDL) was used as a threshold in selecting samples to calculate the MDL. Thus, each of the 12 MDL blends that contained mean reference laboratory concentrations less than 250 ppm were used in calculating MDLs for a given target element. Blends with mean reference laboratory concentrations greater than 250 ppm were discarded for evaluating this objective. For each target element, an MDL was calculated for each sample blend with a mean concentration within the prescribed range. If multiple MDLs could be calculated for an element from different sample blends, these results were averaged to arrive at an overall mean MDL for the demonstration. The mean MDL for each target element was then categorized as either low (MDL less than 20 ppm), medium (MDL between 20 and 100 ppm), or high (MDL exceeds 100 ppm). No blends were available to calculate a detection limit for iron because all the blends contained substantial native concentrations of iron. 4.2.2 Primary Objective 2 Accuracy Accuracy was assessed based on a comparison of the results obtained by the XRF instrument with the results from the reference laboratory for each of the 70 blends in the demonstration sample set. The results from the reference laboratory were essentially used as a benchmark in this comparison, and the accuracy of the XRF instrument results was judged against them. The limitations of this approach should be recognized, however, because the reference laboratory results were not actually "true values." Still, there was a high degree of confidence in the reference laboratory results for most elements, as described in Chapter 5. The following data analysis procedure was followed for each of the 13 target elements to assess the accuracy of an XRF instrument: 1. The results for replicate samples within a blend were averaged for both the data from the XRF instrument and the reference laboratory. Since there were 70 sample blends, this step created a maximum of 70 paired results for the assessment. 2. A blend that exhibited one or more non-detect values in either the XRF instrument or the reference laboratory analysis was excluded from the evaluation. 3. A blend was excluded from the evaluation when the average result from the reference laboratory was below a minimum concentration. The minimum concentration for exclusion from the accuracy assessment was identified as the lower limit of the lowest concentration range (Level 1 in Table 3-1), which is about 50 ppm for most elements. 4. The mean result for a blend obtained with the XRF instrument was compared with the corresponding mean result from the reference laboratory by calculating a relative percent difference (RPD). This comparison was carried out for each of the paired XRF and reference laboratory results included in the evaluation (up to 70 pairs) as follows: 25 ------- RPD where MR MD average (MR, MD) = the mean reference laboratory measurement = the mean XRF instrument measurement. 5. Steps 1 through 4 provided a set of up to 70 RPDs for each element (70 sample blends minus the number excluded in steps 1 and 2). The absolute value of each of the RPDs was taken and summary statistics (minimum, maximum, mean and median) were then calculated. 6. The accuracy of the XRF instrument for each target element was then categorized, based on the median of the absolute values of the RPDs, as either excellent (RPD less than 10 percent), good (RPD between 10 percent and 25 percent), fair (RPD between 25 percent and 50 percent), or poor (RPD above 50 percent). 7. The set of absolute values of the RPDs for each instrument and element was further evaluated to assess any trends in accuracy versus concentration. These evaluations involved grouping the RPDs by concentration range (Levels 1 through 3 and 4, as presented in Table 3-1), preparing summary statistics for each range, and assessing differences among the grouped RPDs. The absolute value of the RPDs was taken in step 5 to provide a more sensitive indicator of the extent of differences between the results from the XRF instrument and the reference laboratory. However, the absolute value of the RPDs does not indicate the direction of the difference and therefore does not reflect bias. The populations of mean XRF and mean reference laboratory results were assessed through linear correlation plots to evaluate bias. These plots depict the linear relationships between the results for the XRF instrument and reference laboratory for each target element using a linear regression calculation with an associated correlation coefficient (r2). These plots were used to evaluate the existence of general bias between the data sets for the XRF instrument and the reference laboratory. 4.2.3 Primary Objective 3 Precision The precision of the XRF instrument analysis for each target element was evaluated by comparing the results for the replicate samples in each blend. All 70 blends in the demonstration sample set (including environmental and spiked samples) were included in at least triplicate so that precision could be evaluated across all concentration ranges and across different matrices. The precision of the data for a target element was evaluated for each blend by calculating the mean relative standard deviation (RSD) with the following equation: RSD = SD C 100 where RSD = Relative standard deviation SD = Standard deviation C = Mean concentration. The standard deviation was calculated using the equation: SD = where SD n C_k C = Standard deviation = Number of replicate samples = Concentration of sample K = Mean concentration. The following specific procedure for data analysis was followed for each of the 13 target elements to assess XRF instrument precision: 1. The RSD for the replicate samples in a blend was calculated for both data from the XRF instrument and the reference laboratory. Since there were 70 sample blends, this step created a maximum of 70 paired RSDs for the assessment. 26 ------- 2. A blend that exhibited one or more non-detect values in either the XRF or the reference laboratory analysis was excluded from the evaluation. 3. A blend was excluded from the evaluation when the average result from the reference laboratory was below a minimum concentration. The minimum concentration for exclusion from the precision assessment was identified as the lower limit of the lowest concentration range (Level 1 in Table 3-1), which was about 50 ppm for most elements. 4. The RSDs for the various blends for both the XRF instrument and the reference laboratory were treated as a statistical population. Summary statistics (minimum, maximum, mean and median) were then calculated and compared for the data set as a whole and for the different concentration ranges (Levels 1 through 3 or 4). 5. The precision of the XRF instrument for each target element was then categorized, based on the median RSDs, as either excellent (RSD less than 5 percent), good (RSD between 5 percent and 10 percent), fair (RSD between 10 percent and 20 percent), or poor (RSD above 20 percent). One primary evaluation was a comparison of the mean RSD for each target element between the XRF instrument and the reference laboratory. Using this comparison, the precision of the XRF instrument could be evaluated against the precision of accepted fixed-laboratory methods. Another primary evaluation was a comparison of the mean RSD for each target element between the XRF instrument and the overall average of all XRF instruments. Using this comparison, the precision of the XRF instrument could be evaluated against its peers. 4.2.4 Primary Objective 4 Impact of Chemical and Spectral Interferences The potential in the XRF analysis for spectral interference between adjacent elements on the periodic table was evaluated for the following element pairs: lead/arsenic, nickel/copper, and copper/zinc. The demonstration sample set included multiple blends where the concentration of one of these elements was greater than 10 times the concentration of the other element in the pair to facilitate this evaluation. Interference effects were identified through evaluation of the RPDs for these sample blends, which were calculated according to the equation in Section 4.2.2, since spectral interferences would occur only in the XRF data and not in the reference laboratory data. Summary statistics for RPDs (mean, median, minimum, and maximum) were calculated for each potentially affected element for the sample blends with high relative concentrations (greater than 10 times) of the potentially interfering element. These summary statistics were compared with the RPD statistics for sample blends with lower concentrations of the interfering element. It was reasoned that spectral interference should be directly reflected in increased RPDs for the interference samples when compared with the rest of the demonstration sample set. In addition to spectral interferences (caused by overlap of neighboring spectral peaks), the data sets were assessed for indications of chemical interferences. Chemical interferences occur when the x-rays characteristic of an element are absorbed or emitted by another element within the sample, causing low or high bias. These interferences are common in samples that contain high levels of iron, where low biases for copper and high biases for chromium can result. The evaluations for Primary Objective 4 therefore included RPD comparisons between sample blends with high concentrations of iron (more than 50,000 ppm) and other sample blends. These RPD comparisons were performed for the specific target elements of interest (copper, chromium, and others) to assess chemical interferences from iron. Outliers and subpopulations in the RPD data sets for specific target elements, as identified through graphical means (probability plots and box plots), were also examined for potential interference effects. The software that is included with many XRF instruments can correct for chemical interferences. The results of this evaluation were intended to differentiate the instruments that incorporated effective software for addressing chemical interferences. 27 ------- 4.2.5 Primary Objective 5 Effects of Soil Characteristics The demonstration sample set included soil and sediment samples from nine locations across the U.S. and a corresponding variety of soil types and lithologies. The accuracy and precision statistics (RPD and RSD) were grouped by soil type (sample location) and the groups were compared to assess the effects of soil characteristics. Outliers and subpopulations in the RPD data sets, as identified through graphical means (correlation plots and box plots), were also examined for matrix effects. 4.2.6 Primary Objective 6 Sample Throughput Sample throughput is a calculation of the total number of samples that can be analyzed in a specified time. The primary factors that affect sample throughput are the time required to prepare a sample for analysis, to conduct the analytical procedure for each sample, and to process and tabulate the resulting data. The time required to prepare and to analyze demonstration samples was recorded each day that demonstration samples were analyzed. Sample throughput can also be affected by the time required to set up and calibrate the instrument as well as the time required for quality control. The time required to perform these activities was also recorded during the field demonstration. An overall mean processing time per sample and an overall sample throughput rate was calculated based on the total time required to complete the analysis of the demonstration sample set from initial instrument setup through data reporting. The overall mean processing time per sample was then used as the primary basis for comparative evaluations. 4.2.7 Primary Objective 7 Technology Costs The costs for analysis are an important factor in the evaluation and include the cost for the instrument, analytical supplies, and labor. The observer collected information on each of these costs during the field demonstration. Based on input from each technology developer and from distributors, the instrument cost was established for purchase of the equipment and for daily, weekly, and monthly rental. Some of the technologies are not yet widely available, and the developer has not established rental options. In these cases, an estimated weekly rental cost was derived for the summary cost evaluations based on the purchase price for the instrument and typical rental to purchase price ratios for similar instruments. The costs associated with leasing agreements were also specified in the report, if available. Analytical supplies include sample cups, spoons, x- ray film, Mylarฎ, reagents, and personal protective equipment. The rate that the supplies are consumed was monitored and recorded during the field demonstration. The cost of analytical supplies was estimated per sample from these consumption data and information on unit costs. Labor includes the time required to prepare and analyze the samples and to set up and dismantle the equipment. The labor hours associated with preparing and analyzing samples and with setting up and dismantling the equipment were recorded during the demonstration. The labor costs were calculated based on this information and typical labor rates for a skilled technician or chemist. In addition to the assessment of the above-described individual cost components, an overall cost for a field effort similar to the demonstration was compiled and compared to the cost of fixed laboratory analysis. The results of the cost evaluation are presented in Chapter 8. 4.2.8 Secondary Objective 1 Training Requirements Each XRF instrument requires that the operator be trained to safely set up and operate the instrument. The relative level of education and experience that is appropriate to operate the XRF instrument was assessed during the field demonstration. The amount of specific training required depends on the complexity of the instrument and the associated software. Most developers have established training programs. The time required to complete the developer's training program was estimated and the content of the training was identified. 28 ------- 4.2.9 Secondary Objective 2 Health and Safety The health and safety requirements for operation of the instrument were identified, including any that are associated with potential exposure from radiation and to reagents. Not included in the evaluation were potential risks from exposure to site-specific hazardous materials or physical safety hazards associated with the demonstration site. 4.2.10 Secon dary Objective 3 Portability The portability of the instrument depends on size, weight, number of components, power requirements, and reagents required. The size of the instrument, including physical dimensions and weight, was recorded (see Chapter 6). The number of components, power requirements, support structures, and reagent requirements were also recorded. A qualitative assessment of portability was conducted based on this information. 4.2.11 Secon dary Objective 4 Durability The durability of the instrument was evaluated by gathering information on the warranty and expected lifespan of the radioactive source or x-ray tube. The ability to upgrade software or hardware also was evaluated. Weather resistance was evaluated if the instrument is intended for use outdoors by examining the instrument for exposed electrical connections and openings that may allow water to penetrate. 4.2.12 Secon dary Objective 5 Availability The availability of the instrument from the developer, distributors, and rental agencies was documented. The availability of replacement parts and instrument- specific supplies was also noted. 4.3 Deviations from the Demonstration Plan Although the field demonstration and subsequent data evaluations generally followed the Demonstration and Quality Assurance Project Plan (Tetra Tech 2005), there were some deviations as new information was uncovered or as the procedures were reassessed while the plan was executed. These deviations are documented below for completeness and as a supplement to the demonstration plan: 1. An in-process audit of the reference laboratory was originally planned while the laboratory was analyzing the demonstration samples. However, the reference laboratory completed all analysis earlier than expected, during the week of the field demonstration, and thereby created a schedule conflict. Furthermore, it was decided that the original pre-award audit was adequate for assessing the laboratory's procedures and competence. 2. The plan suggested that each result for spiked samples from the reference laboratory would be replaced by the "certified analysis" result, which was quantitative based on the amount of each element spiked, whenever the RPD between these two results was greater than 10 percent. The project team agreed that 10 percent was too stringent for this evaluation, however, and decided to use 25 percent RPD as the criterion for assessing reference laboratory accuracy against the spiked samples. Furthermore, it was found during the data evaluations that replacing individual reference laboratory results using this criterion would result in a mixed data set. Therefore, the 25 percent criterion was applied to the overall mean RPD for each element, and the "certified analysis" data set for a specific target element was used as a supplement to the reference laboratory result when this criterion was exceeded. 3. Instrument accuracy and comparability in relation to the reference laboratory (Primary Objective 2) was originally planned to be assessed based on a combination of percent recovery (instrument result divided by reference laboratory result) and RPD. It was decided during the data analysis, however, that the RPD was a much better parameter for this assessment. Specifically, it was found that the mean or median of the absolute values of the RPD for each blend was a good discriminator of instrument performance for this objective. 4. Although this step was not described in the plan, some quantitative results for each instrument were compared with the overall average of all XRF instruments. Since there were eight instruments, it was believed that a comparison of 29 ------- this type did not violate EPA's agreement with the technology developers that one instrument would not be compared with another. Furthermore, this comparison provides an easy- to-understand basis for assessing instrument performance. 5. The plan proposed statistical testing in support of Primary Objectives 4 and 5. Specifically, the Wilcoxon Rank Sum (WRS) test was proposed to assist in evaluating interference effects, and the Rosner outlier test was proposed in evaluating other matrix effects on XRF data quality (EPA 2000; Gilbert 1987). However, these statistical tests were not able to offer any substantive performance information over and above the evaluations based on RPDs and regression plots because of the limited sample numbers and scatter in the data. On this basis, the use of these two statistical tests was not further explored or presented. 30 ------- Chapter 5 Reference Laboratory As described in Chapter 4, a critical part of the evaluation was the comparison of the results obtained for the demonstration sample set by the XRF instrument with the results obtained by a fixed laboratory (the reference laboratory) using conventional analytical methods. Therefore, a significant effort was undertaken to ensure that data of the highest quality were obtained as the reference data for this demonstration. This effort included three main activities: Selection of the most appropriate methods for obtaining reference data, Selection of a high-quality reference laboratory, and Validation of reference laboratory data and evaluation of QA/QC results. This chapter describes the information that confirms the validity, reliability, and usability of the reference laboratory data based on each of the three activities listed above (Sections 5.1, 5.2, and 5.3). Finally, this chapter presents conclusions (Section 5.4) on the level of data quality and the usability of the data obtained by the reference laboratory. 5.1 Selection of Reference Methods Methods for analysis of elements in environmental samples, including soils and sediments, are well established in the environmental laboratory industry. Furthermore, analytical methods appropriate for soil and sediment samples have been promulgated by EPA in the compendium of methods, Test Methods for Evaluating Solid Waste, Physical/Chemical Methods (SW-846) (EPA 1996c). Therefore, the methods selected as reference methods for the demonstration were the SW-846 methods most typically applied by environmental laboratories to soil and sediment samples, as follows: Inductively coupled plasma-atomic emission spectroscopy (ICP-AES), in accordance with EPA SW-846 Method 3050B/6010B, for all target elements except mercury Cold vapor atomic absorption (CVAA) spectroscopy, in accordance with EPA SW-846 Method 7471 A, for mercury only Selection of these analytical methods for the demonstration was supported by the following additional considerations: (1) the methods are widely available and widely used in current site characterizations, remedial investigations, risk assessments, and remedial actions; (2) substantial historical data are available for these methods to document that their accuracy and precision are adequate to meet the objectives of the demonstration; (3) these methods have been used extensively in other EPA investigations where confirmatory data were compared with XRF data; and (4) highly sensitive alternative methods were less suitable given the broad range of concentrations that were inherent in the demonstration sample set. Specific details on the selection of each method are presented below. Element Analysis by ICP-AES. Method 601 OB (ICP-AES) was selected for 12 of the target elements because its demonstrated accuracy and precision meet the requirements of the XRF demonstration in the most cost-effective manner. The ICP-AES method is available at most environmental laboratories and substantial data exist to support the claim that the method is both accurate and precise enough to meet the objectives of the demonstration. Inductively coupled plasma-mass spectrometry (ICP- MS) was considered as a possible analytical technique; however, fewer data were available to support the claims of accuracy and precision. Furthermore, it was available in less than one-third of the laboratories solicited for this project. Finally, ICP-MS is a technique for analysis of trace elements and often requires serial dilutions to mitigate the effect of high concentrations of interfering ions or other matrix interferences. These dilutions can introduce the possibility of error and contaminants that might bias the results. Since the matrices (soil 31 ------- and sediment) for this demonstration are designed to contain high concentrations of elements and interfering ions, ICP-AES was selected over ICP-MS as the instrumental method best suited to meet the project objectives. The cost per analysis is also higher for ICP-MS in most cases than for ICP-AES. Soil/Sediment Sample Preparation by Acid Digestion. The elements in soil and sediment samples must be dissolved from the matrix into an aqueous solution by acid digestion before analysis by ICP-AES. Method 3050B was selected as the preparation method and involves digestion of the matrix using a combination of nitric and hydrochloric acids, with the addition of hydrogen peroxide to assist in degrading organic matter in the samples. Method 3 05 OB was selected as the reference preparation method because extensive data are available that suggest it efficiently dissolves most elements, as required for good overall recoveries and method accuracy. Furthermore, this method was selected over other digestion procedures because it is the most widely used dissolution method. In addition, it has been used extensively as the digestion procedure in EPA investigations where confirmatory data were compared with XRF data. The ideal preparation reference method would completely digest silicaceous minerals. However, total digestion is difficult and expensive and is therefore seldom used in environmental analysis. More common strong acid-based extractions, like that used by EPA Method 3050B, recover most of the heavy element content. In addition, stronger and more vigorous digestions may produce two possible drawbacks: (1) loss of elements through volatilization, and (2) increased dissolution of interfering species, which may result in inaccurate concentration values. Method 3052 (microwave-assisted digestion) was considered as an alternative to Method 3050B, but was not selected because it is not as readily available in environmental laboratories. Soil/Sediment Sample Preparation for Analysis of Mercury by CVAA. Method 7471A (CVAA) is the only method approved by EPA and promulgated for analysis of mercury. Method 7471A includes its own digestion procedure because more vigorous digestion of samples, like that incorporated in Method 3050B, would volatilize mercury and produce inaccurate results. This technique is widely available, and extensive data are available that support the ability of this method to meet the objectives of the demonstration. 5.2 Selection of Reference Laboratory The second critical step in ensuring high-quality reference data was selection of a reference laboratory with proven credentials and quality systems. The reference laboratory was procured via a competitive bid process. The procurement process involved three stages of selection: (1) a technical proposal, (2) an analysis of performance audit samples, and (3) an on- site laboratory technical systems audit (TSA). Each stage was evaluated by the project chemist and a procurement specialist. In Stage 1,12 analytical laboratories from across the U.S. were invited to bid by submitting extensive technical proposals. The technical proposals included: A current statement of qualifications. The laboratory quality assurance manual. Standard operating procedures (SOP) (including sample receipt, laboratory information management, sample preparation, and analysis of elements). Current instrument lists. Results of recent analysis of performance evaluation samples and audits. Method detection limit studies for the target elements. Professional references, laboratory personnel experience, and unit prices. Nine of the 12 laboratories submitted formal written proposals. The proposals were scored based on technical merit and price, and a short list of five laboratories was identified. The scoring was weighed heavier for technical merit than for price. The five laboratories that received the highest score were advanced to stage 2. 32 ------- In stage 2, each of the laboratories was provided with a set of six samples to analyze. The samples consisted of three certified reference materials (one soil and two sediment samples) at custom spiking concentrations, as well as three pre-demonstration soil samples. The results received from each laboratory were reviewed and assessed. Scoring at this stage was based on precision (reproducibility of results for the three pre-demonstration samples), accuracy (comparison of results to certified values for the certified reference materials), and completeness of the data package (including the hard copy and electronic data deliverables). The two laboratories that received the highest score were advanced to stage 3. In stage 3, the two candidate laboratories were subjected to a thorough on-site TSA by the project chemist. The audit consisted of a direct comparison of the technical proposal to the actual laboratory procedures and conditions. The audit also tracked the pre-demonstration samples through the laboratory processes from sample receipt to results reporting. When the audit was conducted, the project chemist verified sample preparation and analysis for the three pre-demonstration samples. Each laboratory was scored on identical checklists. The reference laboratory was selected based on the highest overall score. The weights of the final scoring selection were as follows: Scoring Element Audits (on site) Performance evaluation samples, including data package and electronic data deliverable Price Relative Importance 40% 50% 10% Based on the results of the evaluation process, Shealy Environmental Services, Inc. (Shealy), of Cayce, South Carolina, received the highest score and was therefore selected as the reference laboratory. Shealy is accredited by the National Environmental Laboratory Accreditation Conference (NELAC). Once selected, Shealy analyzed all demonstration samples (both environmental and spiked samples) concurrently with the developers' analysis during the field demonstration. Shealy analyzed the samples by ICP-AES using EPA SW-846 Method 3 05 OB/601 OB and by CVAA using EPA SW-846 Method 7471 A. 5.3 QA/QC Results for Reference Laboratory All data and QC results from the reference laboratory were reviewed in detail to determine that the reference laboratory data were of sufficiently high quality for the evaluation. Data validation of all reference laboratory results was the primary review tool that established the level of quality for the data set (Section 5.3.1). Additional reviews included the on-site TSA (Section 5.3.2) and other evaluations (Section 5.3.3). 5.3.1 Reference Laboratory Data Validation After all demonstration samples had been analyzed, reference data from Shealy were fully validated according to the EPA validation document, USEPA Contract Laboratory Program National Functional Guidelines for Inorganic Data Review (EPA 2004c) as required by the Demonstration and Quality Assurance Project Plan (Tetra Tech 2005). The reference laboratory measured 13 target elements, including antimony, arsenic, cadmium, chromium, copper, iron, lead, mercury, nickel, selenium, silver, vanadium, and zinc. The reference laboratory reported results for 22 elements at the request of EPA; however, only the data for the 13 target elements were validated and included in data comparisons for meeting project objectives. A complete summary of the validation findings for the reference laboratory data is presented in Appendix C. In the data validation process, results for QC samples were reviewed for conformance with the acceptance criteria established in the demonstration plan. Based on the validation criteria specified in the demonstration plan, all reference laboratory data were declared valid (were not rejected). Thus, the completeness of the data set was 100 percent. Accuracy and precision goals were met for most of the QC samples, as were the criteria for comparability, representativeness, and sensitivity. Thus, all reference laboratory data were deemed usable for comparison to the data obtained by the XRF instruments. 33 ------- Only a small percentage of the reference laboratory data set was qualified as undetected as a result of blank contamination (3.3 percent) and estimated because of matrix spike and matrix spike duplicate (MS/MSD) recoveries (8.7 percent) and serial dilutions results (2.5 percent). Table 5.1 summarizes the number of validation qualifiers applied to the reference laboratory data according to QC type. Of the three QC types, only the MS/MSD recoveries warranted additional evaluation. The MS/MSD recoveries for antimony were marginally low (average recovery of 70.8 percent) when compared with the QC criterion of 75 to 125 percent recovery. It was concluded that low recoveries for antimony are common in analysis of soil and sediment by the prescribed methods and likely result from volatilization during the vigorous acid digestion process or spectral interferences found in soil and sediments matrices (or both). In comparison to antimony, high or low recoveries were observed only on an isolated basis for the other target metals (for example, lead and mercury) such that the mean and median percent recoveries were well within the required range. Therefore, the project team decided to evaluate the XRF data against the reference laboratory data for all 13 target elements and to evaluate the XRF data a second time against the ERA certified spike values for antimony only. These comparisons are discussed in Section 7.1. However, based on the validation of the complete reference data set and the low occurrence of qualified data, the reference laboratory data set as a whole was declared of high quality and of sufficient quality to make valid comparisons to XRF data. 5.3.2 Refer en ce Laboratory Techn ical Systems Audit The TSA of the Shealy laboratory was conducted by the project chemist on October 19, 2004, as part of the selection process for the reference laboratory. The audit included the review of element analysis practices (including sample preparation) for 12 elements by EPA Methods 3 05 OB and 601 OB and for total mercury by EPA Method 7471 A. All decision- making personnel for Shealy were present during the TSA, including the laboratory director, QA officer, director of inorganics analysis, and the inorganics laboratory supervisor. Project-specific requirements were reviewed with the Shealy project team as were all the QA criteria and reporting requirements in the demonstration plan. It was specifically noted that the demonstration samples would be dried, ground, and sieved before they were submitted to the laboratory, and that the samples would be received with no preservation required (specifically, no chemical preservation and no ice). The results of the performance audit were also reviewed. No findings or nonconformances that would adversely affect data quality were noted. Only two minor observations were noted; these related to the revision dates of two SOPs. Both observations were discussed at the debriefing meeting held at the laboratory after the TSA. Written responses to each of the observations were not required; however, the laboratory resolved these issues before the project was awarded. The auditor concluded that Shealy complied with the demonstration plan and its own SOPs, and that data generated at the laboratory should be of sufficient and known quality to be used as a reference for the XRF demonstration. 5.3.3 Other Reference Laboratory Data Evaluations The data validation indicated that all results from the reference laboratory were valid and usable for comparison to XRF data, and the pre-demonstration TSA indicated that the laboratory could fully comply with the requirements of the demonstration plan for producing data of high quality. However, the reference laboratory data were evaluated in other ways to support the claim that reference laboratory data are of high quality. These evaluations included the (1) assessment of accuracy based on ERA- certified spike values, (2) assessment of precision based on replicate measurements within the same sample blend, and (3) comparison of reference laboratory data to the initial characterization data that was obtained when the blends were prepared. Each of these evaluations is briefly discussed in the following paragraphs. Blends 46 through 70 of the demonstration sample set consisted of certified spiked samples that were used to assess the accuracy of the reference laboratory data. The summary statistics from 34 ------- comparing the "certified values" for the spiked samples with the reference laboratory results are shown in Table 5-2. The target for percent recovery was 75 to 125 percent. The mean percent recoveries for 12 of the 13 target elements were well within this accuracy goal. Only the mean recovery for antimony was outside the goal (26.8 percent). The low mean percent recovery for antimony supported the recommendation made by the project team to conduct a secondary comparison of XRF data to ERA- certified spike values for antimony. This secondary evaluation was intended to better understand the impacts on the evaluation of the low bias for antimony in the reference laboratory data. All other recoveries were acceptable. Thus, this evaluation further supports the conclusion that the reference data set is of high quality. Table 5-1. Number of Validation Qualifiers Element Antimony Arsenic Cadmium Chromium Copper Iron Lead Mercury Nickel Selenium Silver Vanadium Zinc Totals Number and Percentage of Qualified Results per QC type 1 Method Blank Number 5 12 13 0 1 0 0 68 0 16 22 0 1 138 Percent2 1.5 3.7 4.0 0 0.3 0 0 20.9 0 4.9 6.7 0 0.3 3.3 MS/MSD Number 199 3 0 0 0 0 34 31 0 0 102 0 0 369 Percent2 61.0 0.9 0 0 0 0 10.5 9.5 0 0 31.3 0 0 8.7 Serial Dilution Number 8 10 6 10 8 10 11 4 10 3 7 9 10 106 Percent2 2.4 3.1 1.8 3.1 2.4 3.1 3.4 1.2 3.1 0.9 2.1 2.8 3.1 2.5 Notes: MS Matrix spike. MSB Matrix spike duplicate. QC Quality control. 1 This table presents the number of "U" (undetected) and "J" (estimated) qualifiers added to the reference laboratory data during data validation. Though so qualified, these results are considered usable for the demonstration. As is apparent in the "Totals" row at the bottom of this table, the amount of data that required qualifiers for any specific QC type was invariably less than 10 percent. No reference laboratory data were rejected (that is, qualified "R") during the data validation. 2 Percents for individual elements are calculated based on 326 results per element. Total percents at the bottom of the table are calculated based on the total number of results for all elements (4,238). 35 ------- All blends (1 through 70) were prepared and delivered with multiple replicates. To assess precision, percent RSDs were calculated for the replicate sample results submitted by the reference laboratory for each of the 70 blends. Table 5-3 presents the summary statistics for the reference laboratory data for each of the 13 target elements. These summary statistics indicate good precision in that the median percent RSD was less than 10 percent for 11 out of 13 target elements (and the median RSD for the other two elements was just above 10 percent). Thus, this evaluation further supports the conclusion that the reference data set is of high quality. ARDL, in Mount Vernon, Illinois, was selected as the characterization laboratory to prepare environmental samples for the demonstration. As part of its work, ARDL analyzed several samples of each blend to evaluate whether the concentrations of the target elements and the homogeneity of the blends were suitable for the demonstration. ARDL analyzed the samples using the same methods as the reference laboratory; however, the data from the characterization laboratory were not validated and were not intended to be equivalent to the reference laboratory data. Rather, the intent was to use the results obtained by the characterization laboratory as an additional quality control check on the results from the reference laboratory. A review of the ARDL characterization data in comparison to the reference laboratory data indicated that ARDL obtained lower recoveries of several elements. When expressed as a percent of the average reference laboratory result (percent recovery), the median ARDL result was below the lower QC limit of 75 percent recovery for three elements chromium, nickel, and selenium. This discrepancy between data from the reference laboratory and ARDL was determined to have no significant impact on reference laboratory data quality for three reasons: (1) the ARDL data were obtained on a rapid turnaround basis to evaluate homogeneity accuracy was not a specific goal, (2) the ARDL data were not validated, and (3) all other quality measurement for the reference laboratory data indicated a high level of quality. 5.4 Summary of Data Quality and Usability A significant effort was undertaken to ensure that data of high quality were obtained as the reference data for this demonstration. The reference laboratory data set was deemed valid, usable, and of high quality based on the following: Comprehensive selection process for the reference laboratory, with multiple levels of evaluation. No data were rejected during data validation and few data qualifiers were added. The observations noted during the reference laboratory audit were only minor in nature; no major findings or non-conformances were documented. Acceptable accuracy (except for antimony, as discussed in Section 5.3.3) of reference laboratory results in comparison to spiked certified values. Acceptable precision for the replicate samples in the demonstration sample set. Based on the quality indications listed above, the reference laboratory data were used in the evaluation of XRF demonstration data. A second comparison was made between XRF data and certified values for antimony (in Blends 46 through 70) to address the low bias exhibited for antimony in the reference laboratory data. 36 ------- Table 5-2. Percent Recovery for Reference Laboratory Results in Comparison to ERA Certified Spike Values for Blends 46 through 70 Statistic Number of %R values Minimum %R Maximum %R Mean "/oR1 Median "/oR1 Sb 16 12.0 36.1 26.8 28.3 As 14 65.3 113.3 88.7 90.1 Cd 20 78.3 112.8 90.0 87.3 Cr 12 75.3 108.6 94.3 97.3 Cu 20 51.7 134.3 92.1 91.3 Fe NC NC NC NC NC Pb 12 1.4 97.2 81.1 88.0 Hg 15 81.1 243.8 117.3 93.3 Ni 16 77.0 116.2 93.8 91.7 Se 23 2.2 114.2 89.9 93.3 Ag 20 32.4 100.0 78.1 84.4 V 15 58.5 103.7 90.4 95.0 Zn 10 0.0 95.2 90.6 91.3 Notes: 'Values shown in bold fall outside the 75 to 125 percent acceptance criterion for percent recovery. ERA = Environmental Resource Associates, Inc. NC = Not calculated. %R = Percent recovery. Source of certified values: Environmental Resource Associates, Inc. Sb As Cd Cr Cu Fe Pb Hg Ni Se Ag V Zn Antimony Arsenic Cadmium Chromium Copper Iron Lead Mercury Nickel Selenium Silver Vanadium Zinc 37 ------- Table 5-3. Precision of Reference Laboratory Results for Blends 1 through 70 Statistic Number of %RSDs Minimum %RSD Maximum %RSD Mean %RSDl Median "/oRSD1 Sb 43 1.90 78.99 17.29 11.99 As 69 0.00 139.85 13.79 10.01 Cd 43 0.91 40.95 12.13 9.36 Cr 69 1.43 136.99 11.87 8.29 Cu 70 0.00 45.73 10.62 8.66 Fe 70 1.55 46.22 10.56 8.55 Pb 69 0.00 150.03 14.52 9.17 Hg 62 0.00 152.59 16.93 7.74 Ni 68 0.00 44.88 10.28 8.12 Se 35 0.00 37.30 13.24 9.93 Ag 44 1.02 54.21 12.87 8.89 V 69 0.00 43.52 9.80 8.34 Zn 70 0.99 48.68 10.94 7.54 Notes: 1 Values shown in bold fall outside precision criterion of less than or equal to 25 %RSD. %RSD = Percent relative standard deviation. Based on the three to seven replicate samples included in Blends 1 through 70. Sb As Cd Cr Cu Fe Pb Hg Ni Se Ag V Zn Antimony Arsenic Cadmium Chromium Copper Iron Lead Mercury Nickel Selenium Silver Vanadium Zinc 38 ------- Chapter 6 Technology Description The ElvaX XRF analyzer is manufactured by Elvatech, Ltd. in Kiev, Ukraine and distributed in the United States by Xcalibur XRF Services, Inc. This chapter provides a technical description of the ElvaX based on information obtained from Xcalibur and observation of this analyzer during the field demonstration. This chapter also provides Xcalibur contact information, where additional technical information may be obtained. 6.1 General Description The ElvaX is a portable energy-dispersive XRF analyzer. The ElvaX is capable of detecting elements from sodium (atomic number 11) through plutonium (atomic number 94) and can be applied in the jewelry, metallurgy, customs, forensics, medical diagnostics, food testing, and environmental testing markets. The ElvaX can be used for qualitative or quantitative analysis of metal alloys, liquid food, and biological samples. The ElvaX can analyze liquids and powders as well as samples deposited on surfaces or filters. The ElvaX analyzer system includes two primary components: an XRF spectrometer, and a personal computer. The XRF spectrometer contains a 5-watt x-ray tube excitation source with tungsten, titanium, or rhodium as the anode target material and with an adjustable 4- to 50-kilovolt (kV) power supply. The detector is a Peltier-cooled, solid-state silicon-PiN diode with 180-electron volt (eV) resolution. The XRF spectrometer may be set up in the field but must be in a stable environment. No portable battery systems are currently available for the ElvaX spectrometer. A personal computer (laptop) with Microsoft Windows Millennium Edition (ME) software is used to operate the XRF spectrometer and specifically to select x-ray tube parameters, store data, and provide radiation safety. The laptop is also used to display the x-ray spectrum and to process the data. Some examples of data processing steps included automatic peak search, overlapped peak deconvolution, background removal, automatic element identification, and background subtraction. The ElvaX analyzer can be calibrated using standardless fundamental parameters (FP), site- specific samples, or known standards. An experienced operator can set up the instrument and peripherals and initialize the computer software in 1 to 2 hours, while an inexperienced technician may require 2 to 3 hours. The technical specifications for the ElvaX XRF analyzer are presented in Table 6-1. The ElvaX analyzer is shown in a bench-top configuration in Figure 6-1. Figure 6-1. ElvaX XRF analyzer set up for bench- top analysis. 6.2 Instrument Operations during the Demonstration The ElvaX analyzer and accessories were shipped to the demonstration site in three boxes. The instrument was contained in an overpacked cardboard box with styrofoam padding. The instrument was housed in an aluminum case inside the box for further protection. The peripherals were shipped in two additional cardboard boxes and included some soil standards, the laptop computer, and disposable laboratory supplies. 6.2.1 Set up and Calibration The ElvaX was calibrated using data from pre- demonstration soil samples of known element concentration along with NIST standards. The 39 ------- calibration information was designed to account for differences in sample matrix and to cover the concentration range of elements found in pre- demonstration samples. The ElvaX analyzer was set on a bench and plugged into a 110-volt (V) electrical outlet. After the instrument was connected to an accompanying laptop computer, the ElvaX software was initialized and the pre-demonstration calibration information loaded. The ElvaX detector was allowed to warm up for about 10 minutes before analysis began. The ElvaX software is self-explanatory for instrument start-up; each menu guides the user through the process of turning on the x-ray tube and initializing the spectrometer optics and detector. The elements to be evaluated and their characteristic energy wavelengths and units of measure were selected through the computer software. The calibration of the XRF analyzer was verified by using the calibration reference materials provided with the NIST standards. 6.2.2 Demonstration Sample Processing A two-person field team was provided during the field demonstration to analyze samples using the ElvaX. One field team member was a Ph.D. chemist supplied by the instrument manufacturer (ElvaTech), who operated the instrument. The second field team member was a sales engineer from Xcalibur, who served as the sample processing and data technician. The Xcalibur representative noted that the instrument could be operated by a single trained operator but that a second person was provided for sample preparation so that all samples could be analyzed within the designated week of the field demonstration. Table 6.1. Xcalibur ElvaX XRF Analyzer Technical Specifications Weight: Size: Excitation source: Detector: Signal Processing: Software: Element Range: Power: 18 kilograms (kg) 43 x 34 x 21 centimeters 5-watt x-ray tube; 4 to 50 kV (1 to 100 microamps [|JA]) adjustable power supply; tungsten anode (titanium and rhodium also available); air cooled; 0.14 millimeter (mm) Beryllium window; stability 0.1% over 8 hours. PF-550 from Moxtek, Inc., 7 mm2 Si-PiN, 8 mm beryllium window, Peltier cooled, 180-eV resolution (full width of peak at half maximum height [FWHM]) at 5.9 keV. Multi -channel analyzer; fast-shaping amplifier; pile-up rejection; automatic adaptation to count rate; ADC resolution 4,096 channels, 1032 counts/channel (with successive approximation and "sliding scaling"); real and "live" time. ElvaX menu-driven software (Windows 9x/2000/NT/XP) with USB support for: Instrument control - tube parameters, spectrometric processor, detector temperature, radiation safety, data acquisition, and sample and filter selection. Display - spectra, marker scaling, peak attributes, analysis parameters. Data processing - calibrations, automatic peak search and identification, deconvolution of overlapped peaks, background subtraction, and analytical intensities. Quantitative analysis - standardless FP, FP regression with post processing, full-square regression with standards. From sodium (atomic number 11) through plutonium (atomic number 94). 1 10-220V, 50 hertz (Hz), 50 W. 40 ------- Steps in sample preparation included: Labeling each cup to identify the sample. Filling the sample cup with the homogenized soil or sediment sample (see Figure 6-2). Placing Mylar film on the sample cup with a snap ring to hold the film in place. Gently tapping the inverted sample cup against a hard surface to ensure good contact with the Mylar film and a uniform surface for analysis. Figure 6-2. Xcalibur technician preparing samples for analysis. After these sample preparation steps, the sample cups were passed to the instrument operator and then manually placed in the spectrometer chamber for analysis. One sample was analyzed at a time and required 6 to 8 minutes of instrument run time. A minute or two of additional instrument operator time was needed between each sample analysis to record the data to the personal computer and to reduce the data (Figure 6-3). Once the analysis of a sample batch was completed, the used sample cups were emptied, cleaned, and reused. (This step was needed only because of a shortage of sample cups in the supplies package.) The observer noted that a standard operations manual should be developed that discusses applicable sample media, sample preparation, calibration, and quality control checks for environmental samples. Elvatech and Xcalibur have worked with users of the ElvaX to develop sample preparation and analysis techniques for environmental samples, but these procedures are not well documented. Figure 6-3. Instrument setup during the field demonstration. 6.3 General Demonstration Results The two-person field team analyzed all 326 soil and sediment samples using the ElvaX analyzer in 4.5 days (excluding equipment unpacking, setup, and re- packing), thus averaging 72 samples per day. Routine analysis for this demonstration involved analyzing about six samples per hour (10 minutes per sample), with spectrometer run time varying between 6 and 8 minutes. Analytical results were recorded using the ElvaX computer software developed specifically for the ElvaX analyzer. The data were reduced by the instrument operator using the same software and then transferred to the data technician on a CD for final formatting into an Excel spreadsheet on a second laptop computer. The observer noted that the data processing observed during this demonstration were labor intensive but could be improved, if a tight time deadline were not in place, by using a single operator for all tasks. 6.4 Contact Information Additional information on the ElvaX XRF analyzer is available from the following source: Mr. Ron Williams Xcalibur XRF Services, Inc. 1340 Lincoln Avenue, Unit #6 Holbrook,NY11749 Telephone: (631)435-9749 Cellular: (516) 885-7398 Email: ronupa@aol.com 41 ------- This page was left blank intentionally. 42 ------- Chapter 7 Performance Evaluation As discussed in Chapter 6, Xcalibur analyzed all 326 demonstration samples of soil and sediment at the field demonstration site between January 25 and 29, 2005. (Arrival of Xcalibur staff was delayed by weather, precluding the analysis of any demonstration samples on Monday, January 24, 2005. For this reason, the Xcalibur team remained at the demonstration site until Saturday, January 29, 2005, to complete the sample analyses.) A complete set of electronic data for the ElvaX in Microsoft Excelฎ spreadsheet format was delivered to Tetra Tech when Xcalibur departed from the demonstration site on January 29, 2005. All the data provided by Xcalibur are tabulated and compared with the reference laboratory data and the ERA-certified spike concentrations in Appendix D. The ElvaX data set was reviewed and evaluated in accordance with the primary and secondary objectives of the demonstration. The findings of the evaluation for each objective are presented below. 7.1 Primary Objective 1 Method Detection Limits Samples were selected to calculate MDLs for each target element from the 12 potential MDL sample blends, as described in Section 4.2.1. Xcalibur reported non-detect values as "0", or else reported no result (Appendix D). In selecting samples from among the 12 blends for the calculation of MDLs, blends where one or more of the seven replicates was reported as non-detect were generally not used. In essence, this meant that all seven replicates had to have detected concentrations, as reported by Xcalibur, to calculate an MDL for a blend. Because no blends met this requirement for selenium, one blend was used for the MDL calculation where only six of the seven replicates incorporated detections for selenium. Iron was not included in the MDL evaluation, as was discussed in Section 4.2.1. The MDLs calculated for the ElvaX are presented in Table 7-1. In addition to selenium, only a few MDLs (between one and three) could be calculated for vanadium, mercury, and cadmium. Five or more MDLs could be calculated for the remaining target elements. Also shown in Table 7-1 are the mean MDLs calculated for each target element, which are classified as follows: Very low (1 to 20 ppm): antimony and mercury. Low (20 to 50 ppm): arsenic, copper, nickel, silver, vanadium, and zinc. Medium (50 to 100 ppm): cadmium, chromium, and lead. High (greater than 100 ppm): selenium. The highest mean MDL for a target element was 156 ppm for selenium; no other mean MDLs were above 81 ppm. As noted above, this mean MDL was based on only a single MDL blend and; therefore, is somewhat uncertain. Blend 8 from the Wickes Smelter site produced anomalously high soil MDLs for antimony, cadmium, nickel, and silver. Blend 8 was a roaster slag matrix that contained high concentrations of other potentially interfering elements, such as arsenic, copper, lead, and zinc. Generalized biases in the MDL blend concentrations were also apparent for some elements. For example, the ElvaX reported detections in multiple MDL blends for antimony that were reported as nondetect by the reference laboratory (which used a more sensitive method), indicating the possibility of a generalized high bias at low concentrations for this element. Conversely, the ElvaX reported nondetections for chromium and vanadium in multiple blends where the reference laboratory reported concentrations that should have been detectable by the ElvaX (that is, concentrations near or above the final mean MDL calculated for these elements), indicating a potential low bias. 43 ------- Table 7-1. Evaluation of Sensitivity Method Detection Limits for the Xcalibur ElvaX1 Matrix Soil Soil Soil Soil Soil Soil Soil Sediment Sediment Sediment Sediment Sediment Blend No. 2 5 6 8 10 12 18 29 31 32 39 65 Mean ElvaX MDL Matrix Soil Soil Soil Soil Soil Soil Soil Sediment Sediment Sediment Sediment Sediment Blend No. 2 5 6 8 10 12 18 29 31 32 39 65 Mean ElvaX MDL Antimony ElvaX MDL2 12 3 23 51 11 10 15 16 13 13 11 15 16 ElvaX Cone.3 18 1 33 191 6 64 6 7 6 4 2 6 Ref. Lab Cone4 17 ND 8 118 ND 62 ND ND ND ND ND 11 Copper ElvaX MDL2 11 20 60 NC 24 NC 16 NC NC 30 28 16 25 ElvaX Cone.3 38 65 177 1134 36 852 29 2648 1818 19 62 213 Ref. Lab Cone4 47 49 160 1,243 31 747 50 1986 1514 36 94 69 Arsenic ElvaX MDL2 NC 58 NC NC 47 NC 34 NC 70 16 42 49 45 ElvaX Cone.3 ND 95 382 4289 75 698 67 ND 52 80 60 424 Ref. Lab Cone.4 2 47 477 3,943 39 559 9 10 11 31 14 250 Lead ElvaX MDL2 NC 57 NC NC 91 NC NC 96 87 NC NC 76 81 ElvaX Cone.3 1206 171 8321 54373 115 6562 ND 135 160 ND ND 51 Ref. Lab Cone. 4 1200 78 3986 33,429 72 4,214 17 33 51 26 27 25 Cadmium ElvaX MDL2 NC NC NC 86 NC 46 NC NC NC NC NC 25 52 ElvaX Cone.3 ND ND ND 106 ND 310 ND ND ND ND ND 61 Ref. Lab Cone.4 ND 2 12 91 1 263 ND ND ND ND ND 44 Mercury ElvaX MDL2 NC NC NC NC NC NC 22 NC NC NC NC 17 19 ElvaX Cone.3 ND ND ND ND ND ND 17 ND ND ND ND 12 Ref. Lab Cone.4 ND ND 1 15 0 2 56 0 ND ND ND 32 Chromium ElvaX MDL2 44 NC NC NC 36 63 88 NC 76 NC 74 NC 64 ElvaX Cone.3 204 ND ND ND 84 73 137 ND 114 ND 75 215 Ref. Lab Cone.4 167 121 133 55 116 101 150 63 133 75 102 303 Nickel ElvaX MDL2 25 41 37 80 31 19 41 36 75 36 45 23 41 ElvaX Cone.3 92 48 59 68 67 78 179 110 203 117 142 183 Ref. Lab Cone.4 83 60 70 57 60 91 213 72 196 174 202 214 44 ------- Table 7-1. Evaluation of Sensitivity Method Detection Limits for the Xcalibur ElvaX1 (Continued) Matrix Soil Soil Soil Soil Soil Soil Soil Sediment Sediment Sediment Sediment Sediment Blend No. 2 5 6 8 10 12 18 29 31 32 39 65 Mean ElvaX MDL Selenium ElvaX MDL2 NC NC NC NC NC 156s NC NC NC NC NC NC 156 ElvaX Cone.3 ND ND ND ND ND 71 5 ND ND ND ND ND ND Ref. Lab Cone4 ND ND ND ND ND 15 ND ND ND 5 ND 22 Silver ElvaX MDL2 NC NC 24 120 NC 40 NC NC NC 18 NC 34 47 ElvaX Cone.3 ND ND 26 160 ND 44 ND ND ND 9 ND 46 Ref. Lab Cone.4 ND 1 14 144 ND 38 ND ND 6 ND ND 41 Vanadium ElvaX MDL2 NC 45 NC NC NC NC NC NC NC NC NC NC 45 ElvaX Cone.3 ND 33 ND ND ND ND ND ND ND ND ND ND Ref. Lab Cone. 4 1 55 56 34 51 45 67 96 76 57 38 31 Zinc ElvaX MDL2 28 65 NC NC 61 NC 21 29 19 43 85 NC 44 ElvaX Cone.3 65 368 1085 6364 173 3361 106 177 103 110 208 3425 Ref. Lab Cone.4 24 229 886 5,657 92 2,114 90 160 137 69 137 1,843 Notes: 1 Detection limits and concentrations are in milligrams per kilogram (mg/kg), or parts per million (ppm). 2 MDLs calculated from the 12 MDL sample blends for the ElvaX in this technology demonstration (in bold typeface for emphasis). 3 This column lists the mean concentration reported for this sample blend by the ElvaX. 4 This column lists the mean concentration reported for this sample blend by the reference laboratory. 5 To increase the number of calculated MDLs for this metal, this blend was included despite the fact that detections were reported by the vendor for only six of the seven replicates. This mean concentration and the corresponding MDL were calculated using the five replicated detected concentrations. Cone. Concentration. MDL Method detection limit. NC The MDL was not calculated because reference laboratory concentrations exceeded five times the expected MDL range (approximately 50 ppm, depending on the element) or an insufficient number of detected concentrations were reported. ND One or more results for this blend were reported as "Not Detected." Excepted as noted, blends with one or more ND result as reported by the XRF analyzer were not used for calculating the MDL for this element. Ref. Lab. Reference laboratory. 45 ------- The mean MDLs calculated for the ElvaX are compared in Table 7-2 with the mean MDLs for all XRF instruments that participated in the demonstration and the mean MDLs derived from performance data presented in EPA Method 6200 (EPA 1998e). As shown, the mean MDLs for the ElvaX were lower than the available mean MDLs calculated from EPA Method 6200 data for all elements except lead. When compared with the overall average results for all eight XRF instruments that participated in the demonstration, the ElvaX exhibited high relative mean MDLs for arsenic, lead, selenium, silver, and vanadium. Mean MDLs for the ElvaX were somewhat lower than the all-instrument means for antimony, cadmium, chromium, and nickel. The ElvaX and all-instrument means were essentially equivalent for copper, mercury, and zinc. 7.2 Primary Objective 2 Accuracy and Comparability The number of demonstration sample blends that met the criteria for evaluation of accuracy, as described in Section 4.2.2, ranged from 16 blends for vanadium to 70 blends for iron. RPDs between the mean concentrations obtained from the ElvaX and the reference laboratory were calculated for each blend that met the criteria. Table 7-3 presents the median RPDs for each target element, along with the number of RPD results used to calculate the median. These statistics are provided for all blends as well as for subpopulations grouped by medium (soil versus sediment) and concentration level (Levels 1 through 4, as documented in Table 3-1). Additional summary statistics for the RPDs (minimum, maximum, and mean) are provided in Appendix E (Table E-l). Table 7-2. Comparison of Mean ElvaX MDLs to All-Instrument Mean MDLs and EPA Method 6200 Data1 Notes: i EPA MDL NR Element Antimony Arsenic Cadmium Chromium Copper Lead Mercury Nickel Selenium Silver Vanadium Zinc ElvaX Mean MDLs2 16 45 52 64 25 81 19 41 156 5 47 45 44 All XRF Instrument Mean MDLs3 61 26 70 83 23 40 23 50 8 42 28 38 EPA Method 6200 Mean Detection Limits4 55 5 92 NR 376 171 78 NR 100 5 NR NR NR 89 Detection limits are in units of milligrams per kilogram (mg/kg), or parts per million (ppm). The mean MDLs calculated for this technology demonstration, as presented in Table 7-1. The overall average of the mean MDLs calculated for all eight XRF instruments that participated in this EPA technology demonstration. Mean values calculated from Table 4 of Method 6200 (EPA 1998e, www.epa.gov/sw-846). Only one value reported. U.S. Environmental Protection Agency. Method detection limit. Not reported; no MDLs reported for this element. 46 ------- Accuracy was classified as follows for the target elements based on the overall median RPDs: Very good (median RPD less than 10 percent): None. Good (median RPD between 10 and 25 percent): cadmium, iron, nickel, and silver. Fair (median RPD between 25 percent and 50 percent): antimony, arsenic, chromium, copper, and zinc. Poor (median RPD greater than 50 percent): lead, mercury, selenium, and vanadium. The median RPD was used for this evaluation because it is less affected by extreme values than is the mean. (The initial evaluation of the RPD populations for the demonstration showed that they were generally right-skewed or lognormal.) However, the classification of the elements based on accuracy stayed the same for all target elements except one (silver) when the mean rather than the median RPD was used for the evaluation (Table E-l). Review of the median RPDs revealed few trends with respect to media type (soil versus sediment) or concentration level. The most notable trends are summarized below: Higher overall median RPDs were observed in sediment than in soil for silver, vanadium, and zinc. RPDs were generally high for these metals in sediment blends associated with the Leviathan Mine, Torch Lake, and Ramsey Flats sampling sites. High median RPDs in the soil matrices were observed in the Level 1 samples for arsenic (with concentrations between 50 and 500 ppm). The median RPDs of 58.3 percent at this concentration level (classified in the "poor" range) was much higher than those for higher concentration levels in soil, where the median RPDs were in the "good" range. The high RPDs in the Level 1 soil samples for arsenic appeared to be generalized and not traceable to specific blends or sampling sites. For many other target elements, however, accuracy appeared to decrease with increasing concentration. RPDs for chromium, selenium, and vanadium increased as concentrations increased from the Level 1 to the Level 3 ranges for both soil and sediment. For seven other target elements, RPDs decreased in Level 2 soil and sediment relative to the Level 1 samples, indicating improved accuracy, but then increased again in Level 3 samples. These observations imply that the ElvaX provides the best overall accuracy over a fairly narrow range of moderate element concentrations. Accuracy appears to decline in more complex soil and sediment matrixes with high element concentrations. As an additional basis for comparison, Table 7-3 presents the overall average of the median RPDs for all eight XRF instruments. Complete summary statistics for the RPDs across all eight XRF instruments are included in Appendix E (Table E-l). Table 7-3 indicates that the median RPDs for the ElvaX were equivalent to or below the all-instrument medians for five of the 13 target elements. The median RPDs for the ElvaX were somewhat higher than the all-instrument medians for arsenic, chromium, copper, and zinc, and were significantly higher for lead, mercury, selenium, and vanadium. Section 5.3.3 discussed how the reference laboratory data for antimony were consistently biased low when compared with the ERA-certified spike concentrations. This effect may be caused by volatilization of the antimony compounds used for spiking, resulting in loss of antimony during the sample digestion process at the reference laboratory. Therefore, Table 7-3 includes a second evaluation of accuracy for antimony, comparing the results from the ElvaX with the ERA-certified values. Unlike most of the other XRF instruments that participated in the demonstration, however, use of these values did not improve the RPDs for antimony. The mean RPD for the antimony data set actually increased significantly from 45.5 percent ("fair") to 137.4 percent ("poor") when the ERA-certified values were used. The ElvaX data displayed a consistent low bias for antimony when compared with the ERA-certified spike concentrations. In addition to calculating RPDs, the evaluation of accuracy included preparing linear correlation plots of ElvaX concentration values against the reference laboratory values. These plots are presented for the individual target elements in Figures E-l through E- 13 of Appendix E. The plots include a 45-degree line that shows the "ideal" relationship between the 47 ------- Table 7-3. Evaluation of Accuracy Relative Percent Differences versus Reference Laboratory Data for the Xcalibur ElvaX Matrix Soil Sediment All Samples All Samples Sample Group Level 1 Level 2 Level 3 Level 4 All Soil Level 1 Level 2 Level 3 Level 4 All Sediment Xcalibur ElvaX All XRF Instruments Statistic Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Antimony Ref ERA Lab Spike 9 1 47.0% 154.0% 5 1 31.7% 141.6% 3 2 71.9% 147.7% .. .. 17 4 43.9% 147.7% 3 3 43.8% 114.1% 4 4 38.4% 135.6% 3 3 62.3% 138.7% .. .. 10 10 45.6% 135.6% 27 14 45.5% 137.4% 206 110 84.3% 70.6% Arsenic 15 58.3% 4 15.9% 4 20. 1% - -- 23 45.0% 17 42.5% 4 29.9% 2 49.2% - -- 23 42.5% 46 44.2% 320 26.2% Cadmium 7 16.4% 7 12.4% 2 13.2% - -- 16 13.9% 3 14.0% 4 29.6% 3 17.7% - -- 10 21.7% 26 16.3% 209 16.7% Chromium 23 21.2% 4 39.9% 2 47.9% - -- 29 29.4% 6 20.6% 3 34.6% 3 37.8% - -- 12 32.4% 41 30.7% 338 26.0% Copper 16 62.7% 8 5.7% 2 62.0% - -- 26 26.6% 8 33.0% 4 4.8% 10 27.2% - -- 22 25.1% 48 25. 1% 363 16.2% Iron 5 25.5% 13 10.3% 13 29.1% 7 30.9% 38 24.1% 3 19.2% 19 14.0% 4 23.0% 6 30.6% 32 17.6% 70 19.5% 558 26.0% Lead 7 50.5% 4 36.2% 8 55.5% 5 22.3% 24 47.0% 12 68.1% 3 59.9% 3 81.2% - -- 18 66.9% 42 54.6% 392 21.5% Mercury 5 107.9% 7 90.4% 2 115.7% - -- 14 96.2% 3 89.8% 4 79.2% 3 88.5% - -- 10 84.5% 24 90.7% 192 58.6% Nickel 24 16.7% 5 30.9% 6 13.6% - -- 35 17.0% 18 22.1% 6 17.4% 4 18.5% - -- 28 20.0% 63 17.5% 403 25.4% Selenium 2 2.3% 5 72.7% 4 88.3% - -- 11 75.7% 3 20.0% 4 67.7% 3 97.4% - -- 10 69.1% 21 75.7% 195 16.7% Silver 3 11.6% 3 7.6% 7 16.5% - -- 13 12.4% 4 48.6% 4 30.4% 3 68.3% - -- 11 50.3% 24 18.3% 177 28.7% Vanadium 3 35.4% 3 70.6% 4 78.6% - -- 10 67.4% 0 NC 3 74.2% 3 83.3% - -- 6 79.5% 16 74.0% 218 38.3% Zinc 20 21.6% 6 35.2% 9 22.2% - -- 35 22.3% 17 33.9% 5 50.8% 4 30.6% - -- 26 37.2% 61 32.5% 471 19.4% Notes: All median RPDs presented in this table are based on the population of absolute values of the individual RPDs. No samples reported by the reference laboratory in this concentration range. ERA Environmental Resource Associates, Inc. Number Number of samples appropriate for accuracy evaluation. Ref Lab Reference laboratory (Shealy Environmental Services, Inc.) RPD Relative percent difference. 48 ------- ElvaX data and the reference laboratory data, as well as a "best fit" linear equation (y = mx + b, where m is the slope of the line and b is the y-intercept of the line) and correlation coefficient (r2) to help illustrate the "actual" relationship between the two methods. To be considered accurate, the correlation coefficient should be greater than 0.9, the slope (m) should be between 0.75 and 1.25, and the y-intercept (b) should be relatively close to zero (that is, plus or minus the mean MDL in Table 7-1). Table 7-4 lists the results for these three correlation parameters and highlights in bold each target element that met all three accuracy criteria. This table shows that the results for arsenic, cadmium, and nickel met all three of these criteria. The correlation plot for nickel is displayed in Figure 7-1 as an example of the correlations obtained for these elements. 3500 -i TflOO 2500 - p. fa pi 2000 X 03 > 3 1500 - 3 a ra u X 1000 500 - n c Figure 7-1. Linear correlation plot for ElvaX showing high correlation for nickel. ] I Xcalibur ElvaX 1 i 45 Deerees 1 1 I Linear (Xcalibur ElvaX) ^ m ^ ' J m S 1 *" *" ' ^ y = 0.85x+ 15.5l| ^^ R2 = 0.99 1 ^ ^^^^^1 ;>-' ..--- . ,-- ' ^ I mmS* ^r^ 500 1000 1500 2000 2500 3000 3500 Reference Laboratory (ppm) 49 ------- Table 7-4. Summary of Correlation Evaluation for the ElvaX Target Element Antimony (vs. Reference Lab) Antimony (vs. ERA Certified Value) Arsenic Cadmium Chromium Copper Iron Lead Mercury Nickel Selenium Silver Vanadium Zinc m 0.44 0.15 1.23 1.24 0.62 1.59 0.67 1.40 0.19 0.85 2.99 1.28 0.33 1.03 b 50.8 19.4 35.1 -24.9 34.9 -212.6 5071. 9 2 -324.1 113.6 15.5 -97.0 30.0 25.8 223.1 r2 0.83 0.98 0.97 0.98 0.98 0.93 0.93 0.94 0.82 0.99 0.96 0.63 0.80 0.85 Correlation Moderate High High High High High High High Moderate High High Moderate Moderate Moderate Bias Low1 Low Low High Low High Low High High Low ~ Notes: b m o Although the overall bias for antimony was low, a high bias was indicated at low concentrations by the high relative y-intercept. This high bias was noted as part of the MDL evaluation in Section 7.1. For iron, no MDL was calculated and the high intercept value was the result of the extreme range of concentrations in the demonstration samples. No bias observed. Y-intercept of correlation line. Slope of correlation line. Correlation coefficient of correlation line. General observations from the correlation plots are as follows: A moderate degree of correlation and a somewhat low overall bias were observed between the data for the ElvaX and the reference laboratory for antimony. Table 7-4 and Figure E-l show a second correlation analysis for antimony, comparing the mean ElvaX concentrations for spiked blends with the ERA-certified values. Although a slightly better correlation was observed relative to the ERA-certified values (r2 improved from 0.83 to 0.98), a much lower slope of 0.15 indicates a significant low bias in the ElvaX data when compared with these values. This observation was consistent with the RPD evaluation and showed that, unlike many other XRF instruments in the demonstration, comparisons to ERA-certified concentrations did not improve the apparent accuracy of the ElvaX data for antimony. Large y-intercepts were calculated for lead and iron. Examination of the plots for these elements (Figures E-6 and E-7) reveals that these y- intercepts are small relative to the extreme range of concentrations in the demonstration samples. Smaller but significant y-intercepts were also observed for copper and zinc. However, these intercepts were again small enough relative to the concentration range of the demonstration samples to have a minor effect on the overall correlation and bias observed for these metals. Mercury exhibited a moderate r2 value (0.82) and a low bias (m = 0.19). Removing two extreme Level 4 concentrations (Blends 21 and 22) from the plots produced a poorer correlation coefficient 50 ------- (in the range of 0.64) without improving the low bias. Similar instrument performance (moderate correlation with a significant low bias) was also observed for vanadium. According to the developer, interference from titanium (which was not characterized in the demonstration and therefore could not be adjusted for) affected instrument accuracy for vanadium (Appendix B). Significant high biases were observed for selenium, lead, and copper. Whereas the bias appeared to be generalized for selenium (Figure E-10), the bias observed for lead and copper appeared to be influenced by the extremely high concentrations of a few sample blends. These blends were generally associated with the Wickes Smelter site (Blends 7 through 9 and 51), along with one blend from the Alton Steel site (Blend 53). Although no bias was observed for zinc, removal of another high-concentration outlier from the Alton Steel site (Blend 17) improved the correlation coefficient for zinc from 0.85 to 0.97. The lowest degree of correlation (r2 = 0.63) was observed for silver, and appeared to be caused by broad variability in the data rather than a few outliers. Figure 7-2 shows the correlation plot for silver. In conclusion, the evaluations of accuracy showed an acceptable overall level of performance by the ElvaX for the target elements. Correlations with the reference laboratory were generally high and, for most target elements, the median RPDs for the ElvaX were equivalent or better than the overall median of all eight XRF instruments that participated in the demonstration. However, the ElvaX showed significant biases for some elements, and accuracy tended to decrease in high concentration samples and complex matrixes. In addition, ElvaX results for antimony did not agree with the certified spike concentrations in the spiked sample blends, showing a low bias. Although some pre-demonstration samples were used in the initial calibration process on the first day of the demonstration, it is possible that the ElvaX 500 - g, 400 - e. X 9 a a 200 - 100 Q C s Fig. Xcalibur ElvaX 45 Degrees Linear (Xcalibur ElvaX) , _ *'"'* '" ^m** f S* m 50 100 ire 7-2. Linear correlation plot for ElvaX showing high data variability for silver. S ^ m m S m s ' i L50 200 250 300 350 400 Reference Laboratory (ppm) y = 1.28x R2 = ( 4? + 29.99J ).63 1 0 51 ------- analysis procedures and quantitation algorithms (which were developed for broad-based and not specifically for environmental applications) may have limited instrument accuracy. Development of a detailed standard operating procedure (SOP) and an instrument set-up that are more targeted to environmental soil and sediment samples might improve the comparability of the ElvaX data with that of the reference laboratory. 7.3 Primary Objective 3 Precision As described in Section 4.2.3, the precision of the ElvaX was evaluated by calculating RSDs for the replicate measurements from each sample blend. Median RSDs for the various concentration levels and media (soil and sediment), as well as for the demonstration sample set as a whole, are presented in Table 7-5. An expanded set of summary statistics for the RSDs (including minimum, maximum, and mean) is provided in Appendix E (Table E-2). The median RSDs calculated for the target elements ranged as high as 24.5 percent (vanadium). The ranges of median RSDs are further summarized below: Very low (median RSD between 0 and 5 percent): copper and iron. Low (median RSD between 5 and 10 percent): antimony, cadmium, lead, nickel, selenium, silver, and zinc. Moderate (median RSD between 10 and 20 percent): arsenic, chromium, and mercury. High (median RSD greater than 20 percent): vanadium. The high overall level of precision may have been facilitated by the level of processing (homogenizing, sieving, crushing, and drying) on the sample blends before the field demonstration (Chapter 3). This observation is consistent with the previous SITE MMT program demonstration of XRF technologies that occurred in 1995 (EPA 1996a, 1996b, 1998a, 1998b, 1998c, and 1998d). The high level of sample processing applied during both XRF technology demonstrations was necessary to minimize the effects of sample heterogeneity on the demonstration results and on comparability with the reference laboratories. During project design, site investigation teams that intend to compare XRF and laboratory data should similarly assess the need for sample processing steps to manage sample heterogeneity and improve data comparability. Further review of the median RSDs in Table 7-5 based on concentration range reveals higher RSDs (in other words, lower precision) for the target elements in Level 1 samples when compared with the rest of the data set. This effect was observed for most of the target elements in both soil and sediment, with large relative effects for cadmium, chromium, mercury, selenium, and vanadium. This observation indicates that analytical precision for the ElvaX may depend on concentration. As an additional comparison, Table 7-5 presents the overall average of the median RSDs for all eight XRF instruments that participated in the demonstration. Complete summary statistics for the RSDs across all eight XRF instruments are included in Table E-2. Table 7-5 indicates that the median RSDs for the ElvaX were equivalent to or above the all-instrument medians, indicating equivalent or lower precision, for 12 of the 13 target elements. Slightly lower median RSDs for the ElvaX than the all-instrument medians were observed for antimony. Table 7-6 presents median RSD statistics for the reference laboratory and compares these with the summary data for the ElvaX. (Complete summary statistics are provided in Table E-3 of Appendix E.) For seven of the 13 target elements, Table 7-6 indicates that the median RSDs for the ElvaX were equivalent to or lower than the RSDs for the reference laboratory. The ElvaX exhibited higher RSDs than the reference laboratory for arsenic, chromium, mercury, selenium, silver, and vanadium. Thus, the ElvaX exhibited slightly better precision overall than the reference laboratory. In comparison to the ElvaX, the median RSDs for all XRF instruments were equivalent to or lower than for the reference laboratory for 11 of 13 target elements. 52 ------- Table 7-5. Evaluation of Precision Relative Standard Deviations for the Xcalibur ElvaX Matrix Soil Sediment All Samples All Samples Sample Group Level 1 Level 2 Level 3 Level 4 All Soil Level 1 Level 2 Level 3 Level 4 All Sediment Xcalibur ElvaX A11XRF Instruments Statistic Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Antimony 9 6.7% 5 3.0% 3 3.6% 17 6.5% 3 5.1% 4 6.3% 3 3.4% 10 5.2% 27 5.4% 206 6.1% Arsenic 15 16.1% 4 7.7% 4 16.0% 23 14.8% 17 18.5% 4 4.6% 2 2.2% 23 14.1% 46 14.1% 320 8.2% Cadmium 7 20.5% 7 2.2% 2 4.5% 16 6.3% 3 8.1% 4 5.5% 3 3.2% 10 6.5% 26 6.5% 209 3.6% Chromium 23 20.9% 4 5.5% 2 2.4% 29 17.7% 6 30.0% 3 5.4% 3 5.0% 12 12.5% 41 17.2% 338 12.1% Copper 16 6.2% 8 3.8% 2 12.8% 26 6.0% 8 6.1% 4 2.3% 10 4.3% 22 4.3% 48 4.9% 363 5.1% Iron 5 4.4% 13 2.7% 13 3.8% 7 4.5% 38 4.1% 3 4.9% 19 2.2% 4 2.4% 6 3.2% 32 2.5% 70 3.2% 558 2.2% Lead 7 7.0% 4 4.2% 8 2.6% 5 10.4% 24 4.6% 12 12.5% 3 3.2% 3 2.7% 18 6.4% 42 6.0% 392 4.9% Mercury 5 37.7% 7 12.6% 2 6.3% 14 15.7% 3 42.8% 4 5.9% 3 5.2% 10 6.5% 24 12.5% 192 6.8% Nickel 24 10.3% 5 6.3% 6 2.6% 35 7.9% 18 9.9% 6 5.9% 4 1.8% 28 8.2% 63 8.0% 403 7.0% Selenium 2 27.0% 5 5.2% 4 8.3% 11 8.5% 3 17.3% 4 9.6% 3 3.6% 10 9.6% 21 8.9% 195 4.5% Silver 3 11.5% 3 7.3% 7 19.2% 13 11.5% 4 9.4% 4 5.6% 3 3.2% 11 7.0% 24 9.4% 177 5.2% Vanadium 3 49.4% 3 23.3% 4 28.9% 10 39.9% 0 NC 3 25.7% 3 5.6% 6 12.1% 16 24.5% 218 8.5% Zinc 20 8.1% 6 2.3% 9 1.8% 35 6.4% 17 8.3% 5 3.3% 4 1.8% 26 5.8% 61 6.1% 471 5.3% Notes: Number RSD No samples reported by the reference laboratory in this concentration range. Number of samples appropriate for precision evaluation. Relative standard deviation 53 ------- Table 7-6. Evaluation of Precision - Relative Standard Deviations for the Reference Laboratory versus the ElvaX and All Demonstration Instruments Matrix Soil Sediment All Samples All Samples All Samples Sample Group Ref. Lab Ref. Lab Ref. Lab Xcalibur ElvaX A11XRF Instruments Statistic Number Median Number Median Number Median Number Median Number Median Antimony 17 9.8% 7 9.1% 24 9.5% 27 5.4% 206 6.1% Arsenic 23 12.4% 24 9.2% 47 9.5% 46 14.1% 320 8.2% Cadmium 15 9.0% 10 8.2% 25 9.0% 26 6.5% 209 3.6% Chromium 34 10.6% 26 7.5% 60 8.4% 41 17.2% 338 12.1% Copper 26 9.1% 21 8.9% 47 8.9% 48 4.9% 363 5.1% Iron 38 8.7% 31 8.1% 69 8.5% 70 3.2% 558 2.2% Lead 33 13.2% 22 7.4% 55 8.6% 42 6.0% 392 4.9% Mercury 16 6.6% 10 6.9% 26 6.6% 24 12.5% 192 6.8% Nickel 35 10.0% 27 7.3% 62 8.2% 63 8.0% 403 7.0% Selenium 13 7.1% 12 7.6% 25 7.4% 21 8.9% 195 4.5% Silver 13 7.5% 10 6.6% 23 7.1% 24 9.4% 177 5.2% Vanadium 21 6.6% 17 8.1% 38 7.2% 16 24.5% 218 8.5% Zinc 35 9.1% 27 6.9% 62 7.4% 61 6.1% 471 5.3% 54 ------- 7.4 Primary Objective 4 Impact of Chemical and Spectral Interferences The RPD data from the accuracy evaluation were further processed to assess the effects of interferences. The RPD data for elements considered susceptible to interferences were grouped and compared based on the relative concentrations of potentially interfering elements. Of specific interest for the comparison were the potential effects of: High concentrations of lead on the RPDs for arsenic, High concentrations of nickel on the RPDs for copper (and vice versa), and High concentrations of zinc on RPDs for copper (and vice versa). The rationale and approach for evaluation of these interferents are described in Section 4.2.4. Interferent-to-element ratios were calculated using the mean concentrations the reference laboratory reported for each blend, classified as low (less than 5X), moderate (5 to 10X), or high (greater than 10X). Table 7-7 presents median RPD data for arsenic, nickel, copper, and zinc that are grouped based on this classification scheme. Complete summary statistics are presented in Appendix E (Table E-4). The tables indicate significant interference effects of zinc on copper. Specifically, as zinc concentrations increased to greater than 10 times the copper concentration, the median RPD for copper increased from 21 percent (within the "good" range defined in Section 7.2) to 99 percent (in the "poor" range). Slight effects were also observed for copper as an interferent for nickel; as copper concentrations increased to greater than 10 times the nickel concentration, the median RPD for nickel increased from 17 percent ("good") to 28 percent ("fair"). Evaluation of the effects of lead on arsenic, nickel on copper, and copper on zinc did not appear to show any consistent trends. In presenting statistics for the raw RPDs as well as the absolute values of the RPDs, Table E-4 further shows that the interferences from zinc appeared to produce an increasingly high bias in the copper data (as indicated by more negative raw RPDs). A similar trend was observed in the effect of copper on nickel. 7.5 Primary Objective 5 Effects of Soil Characteristics The population of RPDs between the results obtained from the ElvaX and the reference laboratory was further evaluated against sampling site and soil type. Separate sets of summary statistics were developed for the mean RPDs associated with each sampling site for comparison to the other sites and to the data set for all samples. The site-specific median RPDs are presented in Table 7-8, along with descriptions of soil or sediment type from observations during sampling at each site. Complete RPD summary statistics for each soil type (minimum, maximum, and mean) are presented in Table E-5 of Appendix E. Another perspective on the effects of soil type was developed by graphically assessing outliers and extreme values in the RPD data sets for each target element. This evaluation focused on correlating these extreme values with sample types or locations for multiple elements across the data set. Some outliers and extreme values are apparent in the correlation plots (Figures E-l through E-13) and are further depicted for the various elements on box and whisker plots in Figure E-14. Review of Table 7-8 indicates that the median RPDs were highly variable and that trends or differences between sample sites were difficult to discern. Evaluations relative to sampling site were further complicated by the low numbers of samples for many target elements. (Table 7-8 indicates that only one to three samples were available from many sampling sites for evaluation of specific target elements.) Extreme RPDs were observed in Alton Steel blends for copper and zinc, the Leviathan Mine blends for lead, Torch Lake blends for nickel, and Sulphur Bank blends for copper and silver. Other individual extreme values noted previously for copper and lead were associated with the Wickes Smelter site (Section 7.2). 55 ------- Table 7-7. Effects of Interferent Elements on the RPDs (Accuracy) for Other Target Elements for the Xcalibur ElvaX1 Parameter Interferent/ Element Ratio Number of Samples Median RPD of Target Element 2 Median Interferent Concentration Median Target Element Concentration Lead Effects on Arsenic <5 5-10 >10 29 7 10 45.1% 21.5% 50.6% 152 8802 4699 178 1129 70 Copper Effects on Nickel <5 5-10 >10 44 5 14 17.2% 15.7% 27.6% 73 1143 2298 146 131 122 Nickel Effects on Copper <5 5-10 >10 39 1 8 21.0% 70.7% 49.4% 128 307 1793 852 37 122 Zinc Effects on Copper <5 5-10 >10 35 2 11 21.0% 8.0% 99.1% 177 5169 3528 909 775 332 Copper Effects on Zinc <5 5-10 >10 49 3 9 32.5% 47.1% 31.3% 177 1085 3670 1085 99 103 Notes: 1 Concentrations are reported in units of milligrams per kilogram (mg/kg), or parts per million (ppm). 2 All median RPDs presented in this table are based on the population of absolute values of the individual RPDs. < Less than. > Greater than. RPD Relative percent difference. 56 ------- Table 7-8. Effect of Soil Type on the RPDs (Accuracy) for Target Elements, Xcalibur ElvaX Matrix Soil Soil Soil Soil& Sediment Sediment Sediment Soil Sediment Soil Site AS BN CN KP LV RF SB TL WS All Matrix Description Fine to medium sand (steel processing) Sandy loam, low organic (ore residuals) Sandy loam (burn pit residue) Soil: Fine to medium quartz sand. Sed. : Sandy loam, high organic. (Gun and skeet ranges) Clay /clay loam, salt crust (iron and other precipitates) Silty fine sand (tailings) Coarse sand and gravel (ore and waste rock) Silt and clay (slag-enriched) Coarse sand and gravel (roaster slag) Statistic Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Antimony 4 12.6% 2 68.9% 1 48.2% 4 45.5% 4 59.0% 6 32.9% 3 45.5% 3 47.0% 27 45.5% Arsenic 1 82.6% 7 33.7% 1 66.2% _ 11 53.8% 12 41.8% 5 48.6% 2 36.2% 7 22.2% 46 44.2% Cadmium 3 13.1% 5 10.1% 2 11.7% _ 5 24.9% 5 21.0% 1 16.3% 2 24.1% 3 14.7% 26 16.3% Chromium 2 8.8% 5 43.2% 1 21.2% 4 7.5% 4 41.6% 8 32.4% 10 22.9% 1 15.6% 6 38.7% 41 30.7% Copper 3 83.7% 6 12.1% o 6 21.0% 2 19.2% 4 28.9% 13 11.6% 4 76.1% 7 28.6% 6 9.5% 48 25.1% Iron 3 19.7% 7 10.3% o 5 2.8% 6 15.1% 12 28.4% 13 16.2% 12 33.7% 7 15.7% 7 23.8% 70 19.5% Lead 3 48.1% 6 43.8% 2 51.7% 6 5.3% 4 84.2% 10 59.0% 4 96.4% 7 70.5% 42 54.6% 57 ------- Table 7-8. Effect of Soil Type on RPDs (Accuracy) of Target Elements, Xcalibur ElvaX (Continued) Matrix Soil Soil Soil Soil& Sediment Sediment Sediment Soil Sediment Soil Site AS BN CN KP LV RF SB TL WS All Matrix Description Fine to medium sand (steel processing) Sandy loam, low organic (ore residuals) Sandy loam (burn pit residue) Soil: Fine to medium quartz sand. Sed. : Sandy loam, high organic. (Gun and skeet ranges) Clay /clay loam, salt crust (iron and other precipitates) Silty fine sand (tailings) Coarse sand and gravel (ore and waste rock) Silt and clay (slag-enriched) Coarse sand and gravel (roaster slag) Statistic Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Number Median Mercury ~ 1 26.6% 2 99.2% ~ 3 88.5% 5 89.8% 10 96.2% 3 79.1% 24 90.7% Nickel Selenium 3 25.8% 6 20.1% o 3 27.6% 3 9.8% 11 14.3% 13 19.9% 11 17.5% 6 36.4% 7 16.3% 63 17.5% 1 68.5% 2 63.4% 2 36.8% ~ 5 84.1% 3 91.7% 3 86.3% 4 51.1% 1 106.0% 21 75.7% Silver 1 16.5% 4 5.1% 2 13.5% ~ 4 22.4% 4 52.6% 1 75.8% 4 46.8% 4 14.3% 24 18.3% Vanadium ~ 2 103.4% 1 70.6% ~ 5 64.2% 3 87.0% 3 35.4% 2 66.9% 16 74.0% Zinc 3 65.0% 7 33.4% o 3 52.2% 2 52.2% 8 34.2% 13 38.4% 11 7.8% 7 31.3% 7 24.9% 61 32.5% Notes: AS Alton Steel Mill BN Burlington Northern railroad/ASARCO East. CN Naval Surface Warfare Center, Crane Division. KP KARS Park - Kennedy Space Center. LV Leviathan Mine/Aspen Creek. RF Ramsey Flats - Silver Bow Creek. SB Sulphur Bank Mercury Mine. TL Torch Lake Superfund Site. WS Wickes Smelter Site. Other Notes: Number RPD No samples reported by the reference laboratory in this concentration range. Number of demonstration samples evaluated. Relative Percent Difference (absolute value). 58 ------- Review of the box and whiskers plot (Figure E-14) and the correlation plots from the accuracy evaluation revealed no other general trends in RPDs relative to sampling site. The outliers and extreme values apparent in Figure E-14 were distributed among six of the nine sampling sites. This evaluation verified the slight prevalence of outliers in the Torch Lake and Sulphur Bank Mine blends. However, sample matrix appeared to have a minor effect on the overall accuracy of the XRF data. The box and whiskers plot in Figure E-14 shows that the broad overall distributions of RPDs precluded the identification of high statistical outliers or extreme values for antimony, arsenic, cadmium, copper, mercury, selenium, and silver. 7.6 Primary Objective 6 Sample Throughput The Elvatech/Xcalibur two-person field team was able to analyze all 326 demonstration samples in 5 days at the demonstration site. Once the ElvaX instrument had been set up and operations had been streamlined, the Elvatech/Xcalibur field team was able to analyze a maximum of 83 samples during an extended work day. This sample throughput was achieved by using the different members of the field team to separately perform the sample preparation and instrumental analysis activities. Without an extended work day, it was estimated that the Elvatech/Xcalibur field team could have only processed 49 samples per day. This estimated sample throughput for a normal working day was lower than that observed for the other instruments that participated in the demonstration (average of 66 samples per day). The lower sample throughput was primarily the result of the long run time in the XRF spectrometer (8 minutes per sample initially). The instrument run time was shortened during the field demonstration to allow sample processing to be completed during the designated week and based on the belief that a reduction in run time could still provide data of sufficient accuracy and precision. If this shorter instrument run time had been implemented at the start of the field demonstration, then the estimated sample throughput for a normal 8-hour work day would have been similar to the average of the other XRF instruments. A detailed discussion of the time required to complete the various steps of sample analysis using the ElvaX is included as part of the labor cost analysis in Section 8.3. 7.7 Primary Objective 7 Technology Costs The evaluations pertaining to this primary objective are described in Chapter 8, Economic Analysis. 7.8 Secondary Objective 1 Training Requirements Technology users must be suitably trained to set up and operate the instrument to obtain the level of data quality required for specific projects. The amount of training required depends on the configuration and complexity of the instrument, along with the associated software. Xcalibur offers on-site training and telephone support to instrument users on an informal, as needed basis. During the demonstration, it was apparent to the observer that the instrument can be operated by a single trained operator. A degreed chemist is advisable but not required to operate the instrument. A second staff member can be added to provide support with sample preparation activities. This second staff member does not require any technical training or expertise. The instrument software includes on-screen prompts to assist the user with instrument setup, operation, and shut-down. The operation manual provided for the demonstration was abbreviated and general, including only a brief presentation of the procedures for instrument set-up, operation, and shut-down. The manual did not include any discussion of sample preparation techniques, quality control requirements, or specific procedures for the analysis of environmental samples. 7.9 Secondary Objective 2 Health and Safety Included in the health and safety evaluation were the potential risks from: (1) potential radiation hazards from the instrument itself, and (2) exposure to any reagents used in preparing and analyzing the samples. However, the evaluation did not include potential risks from exposure to site-specific hazardous materials, such as sample contaminants, or to physical safety hazards. These factors were excluded because of the wide and unpredictable range of sites 59 ------- and conditions that could be encountered in the field during an actual project application of the instrument. The ElvaX appears to be a safe instrument. It uses an x-ray tube that includes two levels of lead shielding between the tube and the operator. In certain modes, compressed helium gas may be used. Proper procedures for the safe handling and use of compressed gas cylinders include the use of hand- trucks for transport, belts for securing the cylinder to a wall or large object for stability, and the use of an appropriate gas regulator. Risks from exposure to radiation, electricity, or reagents are minimal when the manufacturer's recommended operational guidelines are followed. 7.10 Secondary Objective 3 Portability Portability depends on the size, weight, number of components, and power requirements of the instrument, and the reagents required. The size of the instrument, including physical dimensions and weight, is presented in Table 6-1. The number of components, power requirements, support structures, and reagent requirements are also listed in Table 6-1. Two distinctions were made during the demonstration regarding portability: (1) The instrument was considered fully portable if the dimensions were such that the instrument could be easily brought directly to the sample location by one person. (2) The instrument was considered transportable if the dimensions and power requirements were such that the instrument could be moved to a location near the sampling location, but required a larger and more stable environment (for example, a site trailer with AC power and stable conditions). Based on its dimensions and power requirements, the ElvaX is defined as transportable. It is a bench-top unit that can be set on a table or bench in an office or mobile laboratory, or on the back of a truck bed, for field analysis. It is not capable of providing in situ analysis of soil. The instrument is fairly light and compact for a bench-top unit, weighing about 18 kilograms with dimensions of less than 1.5 feet on a side. The only major component other than the XRF instrument itself is the personal computer that houses the operating and data processing systems. Each component requires 110 volts of electricity for operation; no portable battery systems are available at this time. 7.11 Secondary Objective 4 Durability Durability was evaluated by gathering information on the instrument's warranty and the expected lifespan of the radioactive source or x-ray tube. The ability to upgrade software or hardware was also evaluated. Weather resistance was evaluated by examining the instrument for exposed electrical connections and openings that may allow water to penetrate (for portable instruments only). The ElvaX system is constructed from impact- resistant coated metal and molded plastic. However, the instrument is not weather resistant. It must operate in a stable environment; both physical (like a bench-top or firm table) and environmental (free from excessive temperature or moisture extremes). Purchased models include a 1-year parts and labor warranty. The x-ray tube has a lifespan of about 2 to 5 years of normal usage. Upgrades in software are available and are provided at no extra to instrument owners. 7.12 Secondary Objective 5 Availability The ElvaX is manufactured by Elvatech, Ltd., in Kiev, Ukraine. XcaliburXRF Services, Inc., distributes and services the ElvaX from locations on the East and West Coasts of the U.S. and in the Great Lakes region. Xcalibur has a staff of five U.S.-based service technicians and delivers instruments internationally. The company also has a free service line available to access qualified technicians 365 days per year with or without a service contract. The developer indicates that the call-back time on the free service line is less than 20 minutes. 60 ------- Chapter 8 Economic Analysis This chapter provides cost information for the ElvaX XRF analyzer. Cost elements that were addressed included instrument purchase or rental, supplies, labor, and ancillary items. Sources of cost information included input from the technology developer and suppliers as well as observations during the field demonstration. Comparisons are provided to average costs for other XRF technologies and for conventional fixed-laboratory analysis to provide some perspective on the relative cost of using the ElvaX. 8.1 Equipment Costs Capital equipment costs include either purchase or rental of the ElvaX and any ancillary equipment that is generally needed for sample analysis. (See Chapter 6 for a description of available accessories.) Information on price for the analyzer and accessories was obtained from Xcalibur. The base price of the ElvaX instrument, as used at the demonstration, is $35,000. A video camera and helium purge unit can be added for $10,000. An autosampler can also be added to the system for $20,000. Observations during the field demonstration indicated that inclusion of the autosampler accessory could have reduced labor requirements and allowed all sample processing tasks to be performed by one person instead of a two- person team. Purchased models include a 1-year warranty. The lifespan of the x-ray tube is about 2 to 5 years for normal usage. Xcalibur indicated that the ElvaX is not available for rental; however, leasing programs are available. For evaluation purposes later in this chapter an estimated rental cost was derived based on similar XRF technologies where both purchase and rental prices were available. The purchase price, rental cost, and shipping cost for the ElvaX compare favorably the average costs for all XRF instruments that participated in the demonstration, as shown in Table 8-1. Table 8-1. Equipment Costs Cost Element Shipping Capital Cost (Purchase) 2 Weekly Rental Autosampler (for Overnight Analysis) ElvaX $400 $35,000 $1,600 Not Included XRF Demonstration Average 1 $410 $54,300 $2,813 N/A Notes: 1 Average for all eight instruments in the demonstration 2 Does not include the ElvaX autosampler accessory (recommended). N/A Not available or not applicable for this comparison 8.2 Supply Costs The supplies that were included in the cost estimate include sample containers, Mylarฎ film, spatulas or scoops, wipes, and disposable gloves. The rate of consumption for these supplies was based on observations during the field demonstration. Unit prices for these supplies were based on price quotes from independent vendors of field equipment. Additional costs could include helium gas for the helium purge unit. The ElvaX was operated for 5 days to complete the analysis of all 326 samples during the field demonstration. The supplies required to process samples were similar for all XRF instruments that participated in the demonstration and were estimated to cost about $245 for 326 samples or $0.75 per sample. 61 ------- 8.3 Labor Costs Labor costs were estimated based on the total time required by the field team to complete the analysis of all 326 samples and the number of people in the field team, while making allowances for field team members that had responsibilities other than sample processing during the demonstration. For example, some developers sent sales representatives to the demonstration to communicate with visitors and provide outreach services; this type of staff time was not included in the labor cost analysis. While overall labor costs were based on the total time required to process samples, the time required to complete each definable activity was also measured during the field demonstration. These activities included: Initial setup and calibration. Sample preparation. Sample analysis. Daily shutdown and startup. End of proj ect packing. The estimated time required to complete each of these activities using the Elva-X is listed in Table 8- 2. The "total processing time per sample" was calculated as the sum of all these activities assuming that the activities were conducted sequentially; therefore, it represents how much time it would take a single trained analyst to complete these activities. However, the "total processing time per sample" does not include activities that were less definable in terms of the amount of time taken, such as data management and procurement of supplies, and is therefore not a true total. The time to complete each activity using the ElvaX is compared with the average of all XRF instruments in Table 8-2 and with the range of all XRF instruments in Figure 8-1. Specifically, the ElvaX exhibited lower-than-average times for sample preparation and end of project packing, and exhibited higher-than- average times for initial setup and calibration, sample analysis, daily shutdown and startup and total time per sample. Table 8-2. Time Required to Complete Analytical Activities1 Activity Initial Setup and Calibration Sample Preparation Sample Analysis/Data Reduction Daily Shutdown/Startup End of Project Packing Total Processing Time per Sample ElvaX 90 2.2 9.5 30 30 12.2 Average 2 54 3.1 6.7 10 43 10.0 Notes: 1 All estimates are in minutes 2 Average for all eight XRF instruments in the demonstration 62 ------- Initial Set up and Calibration Sample Preparation Sample Analysis Total Processing Time Daily Shut Down/Start Up End of project packing 0 ElvaX ฐ : LJ Range for all eight XRF instruments I 40 60 80 Minutes 100 120 140 Figure 8.1. Comparison of activity times for the ElvaX versus other XRF instruments. The Elvatech/Xcalibur field team expended about 81 labor hours to complete all sample processing activities during the field demonstration using the ElvaX. This was slightly higher than the overall average of 69 hours for all instruments that participated in the demonstration. The primary reasons that labor hours were slightly higher for the ElvaX include: The instrument run time was initially set at about 8 minutes, which was substantially longer than most other instruments. The Elvatech/Xcalibur field team reduced the instrument run time later during the demonstration based on the belief that the longer run time was not needed to obtain good precision and accuracy. The autosampler accessory was not included with the instrument for the demonstration and would have reduced the time spent processing samples through the instrument. 8.4 Comparison of XRF Analysis and Reference Laboratory Costs Two scenarios were evaluated to compare the cost for XRF analysis using the ElvaX with the cost of fixed- laboratory analysis using the reference methods. Both scenarios assumed that 326 samples were to be analyzed, as in the field demonstration. The first scenario assumed that only one element was to be measured in a metal-specific project or application (for example, lead in soil, paint, or other solids) for comparison to laboratory per-metal unit costs. The second scenario assumed that 13 elements were to be analyzed, as in the field demonstration, for comparison to laboratory costs for a full suite of metals. Typical unit costs for fixed-laboratory analysis using the reference methods were estimated using average costs from Tetra Tech's basic ordering agreement with six national laboratories. These unit costs assume a standard turnaround time of 21 days and standard hard copy and electronic data deliverables that summarize results and raw analytical data. No costs were included for field labor that would be specifically associated with off-site fixed laboratory analysis, such as sample packaging and shipment. The cost for XRF analysis using the ElvaX was based on equipment rental for 1 week, along with labor and 63 ------- supplies estimates established during the field demonstration. As noted previously, the estimate used a hypothetical rental rate for the ElvaX based on a survey of rental and purchase costs of similar instruments. This hypothetical rate was used because Xcalibur does not offer a rental program. Labor costs were added for drying, grinding, and homogenizing the samples (estimated at 10 minutes per sample) since these additional steps in sample preparation are required for XRF analysis but not for analysis in a fixed laboratory. A typical cost for managing investigation-derived waste (IDW), including general trash, personal protective equipment, wipes, and soil, was also added to the cost of XRF analysis because IDW costs are included in the unit cost for fixed- laboratory analysis. The IDW management cost was fixed, based on the average IDW disposal cost per instrument during the demonstration, because IDW generation did not vary significantly between instruments during the demonstration. Since the cost for XRF analysis of one element or multiple elements does not vary significantly (all target elements are determined simultaneously when a sample is analyzed), the ElvaX analysis cost was not adjusted for one element versus 13 elements. Table 8-3 summarizes the costs for the ElvaX versus the cost for analysis in a fixed laboratory. This comparison shows that the ElvaX compares favorably to a fixed laboratory in terms of overall cost when a large number of elements are to be determined. The ElvaX compares unfavorably to a fixed laboratory when one element is to be determined. Use of the ElvaX will likely produce additional cost savings because analytical results will be available within a few hours after samples are collected, thereby expediting project decisions and reducing or eliminating the need for additional mobilizations. The total cost for the ElvaX in the example scenario (326 samples) was estimated at $8,436 whether one or a number of elements was analyzed. This estimate compares favorably with the average of $8,932 for all XRF instruments that participated in the demonstration. The ElvaX cost for the example scenario compares very favorably with other bench- top XRF instruments. Table 8-3. Comparison of XRF Technology and Reference Method Costs Analytical Approach ElvaX (1 to 13 elements) Shipping Weekly Rental (estimated)1 Supplies Labor IDW Total ElvaX Analysis Cost (1 to 13 elements) Fixed Laboratory (1 element) (EPA Method 6010, ICP-AES) Total Fixed Laboratory Costs (1 element) Fixed Laboratory (13 elements) Mercury (EPA Method 7471, CVAA) All other Elements (EPA Method 6010, ICP-AES) Total Fixed Laboratory Costs (13 elements) Quantity 1 1 326 135 N/A 326 326 326 Item Roundtrip Week Sample Hours N/A Sample Sample Sample Unit Rate $400 $1,800 $0.75 $43.75 N/A $21 $36 $160 Total $400 $1,800 $245 $5,901 $90 $8,436 $6,846 $6,846 $11,736 $52,160 $63,896 Notes: 1 Extimated values as Xcalibur currently does not have a rental rate for the ElvaX. 64 ------- Chapter 9 Summary of Technology Performance The preceding chapters of this report document that the evaluation design succeeded in providing detailed performance data for the ElvaX XRF analyzer. The evaluation design incorporated 13 target elements, 70 distinct sample blends, and a total of 326 samples. The blends included both soil and sediment samples from nine sampling locations. A rigorous program of sample preparation and characterization, reference laboratory analysis, QA/QC oversight, and data reduction supported the evaluation of XRF instrument performance. One important aspect of the demonstration was the sample blending and processing procedures (including drying, sieving, grinding, and homogenization) that significantly reduced uncertainties associated with the demonstration sample set. These procedures minimized the impacts of heterogeneity on method precision and on the comparability between XRF data and reference laboratory data. In like manner, project teams are encouraged to assess the effects of sampling uncertainty on data quality and to adopt appropriate sample preparation protocols before XRF is used for large-scale data collection, particularly if the project will involve comparisons to other methods (such as off-site laboratories). An initial pilot-scale method evaluation, carried out in cooperation with an instrument vendor, can yield site-specific SOPs for sample preparation and analysis to ensure that the XRF method will meet data quality needs, such as accuracy and sensitivity requirements. A pilot study can also help the project team develop an initial understanding of the degree of correlation between field and laboratory data. This type of study is especially appropriate for sampling programs that will involve complex soil or sediment matrices with high concentrations of multiple elements because the demonstration found that XRF performance was more variable under these conditions. Initial pilot studies can also be used to develop site-specific calibrations, in accordance with EPA Method 6200, that adjust instrument algorithms to compensate for matrix effects. The findings of the evaluation of the ElvaX for each primary and secondary objective of the technology demonstration are summarized in Tables 9-1 and 9-2. The ElvaX and the average performance of all eight instruments that participated in the XRF technology demonstration are compared in Figure 9-1. The comparison in Figure 9-1 indicates that, when compared with the mean performance of all eight XRF instruments, the ElvaX showed: Better MDLs for four elements, including antimony, cadmium, chromium, and nickel (iron was not included in the MDL evaluation). Better accuracy (lower RPDs) for four target elements, including antimony, iron, nickel, and silver. However, when RPDs for antimony are calculated versus sample spike levels rather than reference laboratory data (which may be biased low), accuracy for antimony is lower than for the program as whole. Better precision (lower RSDs) for one target element (antimony). As a transportable bench-top instrument that requires AC power, the ElvaX must be operated in a mobile laboratory or other stable environment, and cannot be used for in situ soil analysis. Although good overall performance was observed for this instrument, the developer may want to consider whether instrument accuracy and sensitivity could be further improved for environmental applications through refined calibration protocols, quantitation algorithms, or other method modifications that could be documented in a written procedure for soil and sediment analysis. 65 ------- Table 9-1. Summary of Xcalibur ElvaX Performance - Primary Objectives Objective Performance Summary PI: Method Detection Limits Low numbers of detections in the MDL blends produced limited data and therefore, uncertainty in the MDL calculations for cadmium, mercury, selenium, and vanadium. Mean MDLs for the target elements ranged as follows: o MDLs of 1 to 20 ppm: antimony and mercury. o MDLs of 20 to 50 ppm: arsenic, copper, nickel, silver, vanadium, and zinc. o MDLs of 50 to 100 ppm: cadmium, chromium, and lead. o MDLs of greater than 100 ppm: selenium. (This MDL was 156 ppm, and was based on only a single sample blend.) The MDLs calculated for the ElvaX were generally lower than reference MDL data from EPA Method 6200 (higher MDLs were observed only for lead). P2: Accuracy and Comparability Median RPDs relative to reference laboratory data revealed the following, with lower RPDs indicating greater accuracy: o RPDs less than 10 percent: none. o RPDs of 10 to 25 percent: cadmium, iron, nickel, and silver. o RPDs of 25 to 50 percent: antimony, arsenic, chromium, copper, and zinc. o RPDs of greater than 50 percent: lead, mercury, selenium, and vanadium. Data review indicated that the reference laboratory results for some spiked demonstration samples may be biased low for antimony due to the volatility of the spiking compounds used. RPDs for antimony were moderate when the ElvaX data were compared with the reference laboratory data (with a median RPD of 45.5 percent) but increased considerably when compared with certified spike values (where the median RPD was 137.4 percent). Thus, comparison to the spike concentrations did not improve the apparent accuracy of the ElvaX for antimony. Correlation plots relative to reference laboratory data indicated: o High correlation coefficients (greater than 0.9) for eight of the 13 target elements. o Moderate correlation coefficients (between 0.5 and 0.9) for the remaining five elements (antimony, mercury, selenium, vanadium, and zinc). o High biases in the XRF data versus the reference laboratory data for copper, lead, selenium, and silver. Low biases were observed for antimony, chromium, iron, mercury, and vanadium. P3: Precision Median RSDs for sample replicates were as follows, with lower RSDs indicating greater precision: o RSDs below 5 percent: copper and iron. o RSDs between 5 and 10 percent: antimony, cadmium, lead, nickel, selenium, silver, and zinc. o RSDs between 10 and 20 percent: arsenic, chromium, and mercury. o RSDs greater than 20 percent: vanadium. RSDs were slightly higher (that is, precision was lower) in the lowest concentration sample blends for many of the target elements, indicating a slight concentration dependence for precision. For seven of the 13 target elements, median RSDs for the ElvaX were equivalent to or lower than the RSDs calculated for the reference laboratory data, indicating similar to slightly better precision for the ElvaX. 66 ------- Table 9-1. Summary of Xcalibur ElvaX Performance - Primary Objectives (continued) Objective Performance Summary P4: Effects of Sample Interferences High relative concentrations (greater than 10X) of zinc as an interfering element reduced accuracy for copper from "good" (median RPDs less than 25 percent) to "poor" (median RPDs greater 50 percent). Further, the high concentrations of zinc produced an increasingly high bias in copper results. A slight interference effect (decreasing accuracy from good to fair, and an increasing negative bias) were observed for nickel in samples containing high concentrations of copper as an interferent. Evaluation of high concentrations of lead on arsenic, nickel on copper, and copper on zinc did not appear to show significant interference trends. P5: Effects of Soil Type A slight prevalence of outliers was noted for some of the target elements in the Leviathan Mine, Torch Lake, Sulphur Bank Mine, Alton Steel, and Wickes Smelter sample blends. However, sample matrix had a minor effect on the overall accuracy of the ElvaX data given that the ranges of RPDs observed for the target elements were very broad. P6: Sample Throughput With an average sample preparation time of 2.2 minutes and an instrument analysis time of 9.5 minutes per sample, the total sample processing time was 12.2 minutes per sample. A maximum sample throughput of 83 samples per day was achieved during the demonstration during an extended work day. A more typical sample throughput was estimated to be 49 samples per day for an 8- hour work day. Use of the optional autosampler may increase sample throughput. However, throughput would have decreased significantly without a second staff member to perform sample preparation and final data processing, which was labor-intensive. P7: Costs Base purchase cost is about $35,000 for the instrument as equipped in the demonstration. Accessories not used in the demonstration include a video camera and helium purge unit ($10,000), as well as an autosampler ($20,000). The base purchase cost includes training and technical support. The Elvatech/Xcalibur field team expended approximately 81 labor hours to complete the processing of the demonstration sample set (326 samples). In comparison, the average for all participating XRF instruments was 69 man-hours. By approximating a 1-week rental cost (based on similar bench-top instruments) and adding labor and miscellaneous costs for shipping and supplies, a total project cost of $8,436 was estimated for a project the size of the demonstration. In comparison, the project cost averaged $8,932 for all participating XRF instruments and the cost for fixed- laboratory analysis of all samples for 13 elements was $63,896. 67 ------- Table 9-2. Summary of Xcalibur ElvaX Performance - Secondary Objectives Objective Performance Summary SI: Training Requirements A degreed chemist is recommended but not required to operate the ElvaX. A second technician without specific training is also recommended to assist with sample preparation and data processing activities to improve sample throughput. Xcalibur offers unlimited product support throughout the lifetime of the instrument, including telephone support and training as needed. The instrument software includes on-screen prompts to assist the user with instrument setup, operation, and shut-down. However, the operation manual provided for the demonstration was abbreviated and general, and no specific procedures for the preparation or analysis of environmental samples was provided. S2: Health and Safety The ElvaX's x-ray tube is totally encased in two layers of lead shielding, and emits no detectable radiation outside of the instrument cabinet. Purging of the sample chamber with helium requires the safe management of pressurized gas cylinders. S3: Portability Based on dimensions and weight, the ElvaX is a transportable instrument, designed to be used on a table top or possibly a truck bed. The instrument and its laptop computer operating system require 110 volt AC power. S4: Durability The ElvaX's x-ray tube has a lifespan of about 2 to 5 years of normal usage. The instrument is fully warranted for 1 year, and software is upgradeable at no cost. The instrument must be operated in a stable environment, free from excessive temperature and moisture extremes. S5: Availability The ElvaX is manufactured by Elvatech, Ltd., in Kiev, Ukraine. Xcalibur XRF Services, Inc., distributes and services the ElvaX from locations on the east and west coasts of the U.S. and in the Great Lakes region. The ElvaX is available for purchase and long-term leasing; no short-term rental options are currently available. 68 ------- Comparison of Mean MDLs: ElvaX vs. All XRF Instruments c .5 E|vaX Mean MDL _j ! 1 50 DAN Instrument Mean MDL 3 h 1 00 c ^ cn n J~l d~l 1_ * H -ฐ _ i I 1 . 1 , ri tn n Target Element Comparison of Median RPDs: ElvaX vs. All XRF Instruments ฃ ElvaX Median RPD "J" n All Instrument Median RPD c 1 UUvo v in onฐ/ i i 1 3fiO% I j_, ^H r /in^/ ^ 1 g 4U /o J ^ * ^ฐ i r m r in ii r i Target Element I I I 1 JH L JH r I ii 2 30% * ฐ5% C " 3 S 20 /o 2 ^ 15% ^ 5 I = 5% * I 0% Comparison of Median RSDs: ElvaX vs. All XRF Instruments ElvaX Median RSD D All Instrument Median RSD I IrFFI Target Element Figure 9-1. Method detection limits (sensitivity), accuracy, and precision of the ElvaX in comparison to the average of all eight XRF instruments. 69 ------- This page was left blank intentionally. 70 ------- Chapter 10 References Gilbert, R.O. 1987. Statistical Methods for Environmental Pollution Monitoring. Van Nostrand Reinhold, New York. Tetra Tech EM Inc. 2005. Demonstration and Quality Assurance Plan. Prepared for U.S. Environmental Protection Agency, Superfund Innovative Technology Evaluation Program. March. U.S. Environmental Protection Agency (EPA). 1996a. TN Spectrace TN 9000 and TNPb Field Portable X-ray Fluorescence Analyzers. EPA/600/R-97/145. March. EPA. 1996b. Field Portable X-ray Fluorescence Analyzer HNU Systems SEFA-P. EPA/600/R-97/144. March. EPA. 1996c. Test Methods for Evaluating Solid Waste, Physical/Chemical Methods (SW- 846). December. EPA. 1998a. Environmental Technology Verification Report; Field Portable X-ray Fluorescence Analyzer, MetorexX-Met 920-MP. EPA/600/R-97/151. March. EPA. 1998b. Environmental Technology Verification Report; Field Portable X-ray Fluorescence Analyzer, Niton XL Spectrum Analyzer. EPA/600/R-97/150. March. EPA. 1998c. ScitectMAP Spectrum Analyzer Field Portable X-Ray Fluorescence Analyzers. EPA/600/R-97/147. March. EPA. 1998d. Metorex X-MET 920-P and 940 Field Portable X-ray Fluorescence Analyzers. EPA/600/R-97/146. March. EPA. 1998e. EPA Method 6200, from "Test Methods for Evaluating Solid Waste, Physical/Chemical Methods (SW-846), Update IVA. December. EPA. 2000. Guidance for Data Quality Assessment: Practical Methods for Data Analysis. EPA QA/G-9 QAOO Update. EPA/600/R-96/084. July. EPA. 2004a. Innovative Technology Verification Report: Field Measurement Technology for Mercury in Soil and Sediment - Metorex's X-METฎ 2000 X-Ray Fluorescence Technology. EPA/600/R-03/149. May. EPA. 2004b. Innovative Technology Verification Report: Field Measurement Technology for Mercury in Soil and Sediment - Niton's XLi/XLt 700 Series X-Ray Fluorescence Analyzers. EPA/600/R-03/148. May. EPA. 2004c. USEPA Contract Laboratory Program National Functional Guidelines for Inorganic Data Review. Final. OSWER 9240.1-45. EPA 540-R-04-004. October. 71 ------- APPENDIX A VERIFICATION STATEMENT ------- UNITED STATES ENVIRONMENTAL PROTECTION AGENCY Office of Research and Development Washington, DC 20460 SITE Monitoring and Measurement Technology Program Verification Statement TECHNOLOGY TYPE: X-ray Fluorescence (XRF) Analyzer APPLICATION: MEASUREMENT OF TRACE ELEMENTS IN SOIL AND SEDIMENT TECHNOLOGY NAME: ElvaX XRF Analyzer COMPANY: Xcalibur XRF Services ADDRESS: 1340 Lincoln Avenue, Unit #6 Holbrook,NY 11749 Telephone: (631)435-9749 Fax: (516)885-7398 Email: ronupa@aol. com Internet: www.xcaliburxrf.com VERIFICATION PROGRAM DESCRIPTION The U.S. Environmental Protection Agency (EPA) created the Superfund Innovative Technology Evaluation (SITE) Monitoring and Measurement Technology (MMT) Program to facilitate deployment of innovative technologies through performance verification and information dissemination. The goal of this program is to further environmental protection by substantially accelerating the acceptance and use of improved and cost- effective technologies. The program assists and informs those involved in designing, distributing, permitting, and purchasing environmental technologies. This document summarizes the results of a demonstration of the Xcalibur ElvaX bench-top x-ray fluorescence (XRF) analyzer for the analysis of 13 target elements in soil and sediment, including antimony, arsenic, cadmium, chromium, copper, iron, lead, mercury, nickel, selenium, silver, vanadium, and zinc. PROGRAM OPERATION Under the SITE MMT Program, with the full participation of the technology developers, EPA evaluates and documents the performance of innovative technologies by developing demonstration plans, conducting field tests, collecting and analyzing demonstration data, and preparing reports. The technologies are evaluated under rigorous quality assurance protocols to produce well-documented data of known quality. EPA's National Exposure Research Laboratory, which demonstrates field sampling, monitoring, and measurement technologies, selected Tetra Tech EM Inc. as the verification organization to assist in field testing technologies for measuring trace elements in soil and sediment using XRF technology. DEMONSTRATION DESCRIPTION The field demonstration of eight XRF instruments to measure trace elements in soil and sediment was conducted from January 24 through 28, 2005, at the Kennedy Athletic, Recreational and Social (KARS) Park, which is part of the Kennedy Space Center on Merritt Island, Florida. A total of 326 samples were analyzed by each XRF instrument, including the ElvaX, during the field demonstration. These samples were derived from 70 different blends and spiked blends of soil and sediment collected from nine sites across the U.S. The sample blends were thoroughly dried, sieved, crushed, mixed, and characterized before they were used for the demonstration. Some A-l ------- blends were also spiked to further adjust and refine the concentration ranges of the target elements. Between three and seven replicate samples of each blend were included in the demonstration sample set and analyzed by the technology developers during the field demonstration. Shealy Environmental Services, Inc. (Shealy), of Cayce, South Carolina, was selected as the reference laboratory to generate comparative data in evaluation of XRF instrument performance. Shealy analyzed all demonstration samples (both environmental and spiked) concurrently with the developers during the field demonstration. The samples were analyzed by inductively coupled plasma-atomic emission spectroscopy (ICP-AES) using EPA SW- 846 Method 3 05 OB/601 OB and by cold vapor atomic absorption spectroscopy (CVAA) using EPA SW-846 Method 7471A (mercury only). This verification statement provides a summary of the evaluation results for the Xcalibur ElvaX XRF analyzer. More detailed discussion can be found in the Innovative Technology Verification Report - XRF Technologies for Measuring Trace Elements in Soil and Sediment: Xcalibur ElvaX XRF Analyzer (EPA/540/R-06/006). TECHNOLOGY DESCRIPTION XRF spectroscopy is an analytical technique that exposes a solid sample. The x-rays from the source have the appropriate excitation energy that causes elements in the sample to emit characteristic x-rays. A qualitative elemental analysis is possible from the characteristic energy, or wavelength, of the fluorescent x-rays emitted. A quantitative elemental analysis is possible from the number (intensity) of x-rays at a given wavelength. The ElvaX is a transportable energy dispersive XRF analyzer capable of detecting elements from sodium (atomic number [Z] = 11) through plutonium (Z = 94) that has applications in the jewelry, metallurgy, customs, forensics, medical diagnostics, food testing, and environmental testing markets. The ElvaX can be used for qualitative or quantitative analysis of environmental samples, metal alloys, liquid food, biological samples, and powder assays, as well as samples deposited on surfaces or filters. The ElvaX contains a 5 watt x-ray tube with an adjustable power supply (5 to 40 kV) and a choice of three different anode materials (tungsten, titanium, or rhodium). The detector is a Peltier-cooled, solid-state silicon-PiN diode with 180 eV resolution. The instrument operating system runs on a laptop computer using Windowsฎ-based software that has a broad range of data analysis capabilities. The ElvaX analyzer can be calibrated using a standardless fundamental parameters calibration or by using an empirical calibration with known standards or site samples. For this demonstration, the ElvaX was calibrated using pre-demonstration samples from the demonstration sampling sites, along with NIST standards. VERIFICATION OF PERFORMANCE Method Detection Limit (MDL): MDLs were calculated using seven replicate analyses from each of 12 low- concentration sample blends according to the procedure described in Title 40 Code of Federal Regulations (CFR) Part 136, Appendix B, Revision 1.11. A mean MDL was then calculated for each element. The ranges into which the mean MDLs fell for the ElvaX are listed below. Relative Sensitivity High Moderate Low Very Low Mean MDL 1-20 ppm 20 - 50 ppm 50 - 100 ppm > 100 ppm Target Elements Antimony and Mercury. Arsenic, Copper, Nickel, Silver, Vanadium, and Zinc. Cadmium, Chromium, and Lead. Selenium. Notes: ppm = Parts per million. Iron was not included in the MDL evaluation. Accuracy: Accuracy was evaluated based on the agreement of the ElvaX results with the reference laboratory data. Accuracy was assessed by calculating the absolute relative percent difference (RPD) between the mean XRF and the mean reference laboratory concentration for each blend. Accuracy of the ElvaX was classified from high to A-2 ------- very low for the various target elements, as indicated in the table below, based on the overall median RPDs calculated for the demonstration. Relative Accuracy High Moderate Low Very Low Median RPD 0% - 10% 10% - 25% 25% - 50% > 50% Target Elements None. Cadmium, Iron, Nickel, and Silver. Antimony, Arsenic, Chromium, Copper, and Zinc. Lead, Mercury, Selenium, and Vanadium. Accuracy was also assessed through correlation plots between the mean ElvaX and mean reference laboratory concentrations for the various sample blends. Correlation coefficients (r2) for linear regression analysis of the plots are summarized below, along with any significant biases apparent from the plots in the XRF data versus the reference laboratory data. Correlation Bias * "e 0.83 Low Arsenic 0.97 -- Cadmium 0.98 -- Chromium 0.98 Low e. e. o O 0.93 High | 0.93 Low e 0.94 High Mercury 0.82 Low z 0.99 -- Selenium 0.96 High ^ QJ a VI 0.63 High Vanadium 0.80 Low 1 0.85 -- Notes: = No significant bias * Correlation is 0.98 with a lower bias when assessed versus sample spike concentrations Precision: Replicates were analyzed for all sample blends. Precision was evaluated by calculating the standard deviation of the replicates, dividing by the average concentration of the replicates, and multiplying by 100 percent to yield the relative standard deviation (RSD) for each blend. Precision of the ElvaX was classified from high to very low for each target element, as indicated in the table below, based on the overall median RSDs. These results indicated an equivalent or higher level of precision in the ElvaX data than in the reference laboratory data for seven of the 13 target elements. Relative Precision High Moderate Low Very Low Median RSD 0% - 5% 5% - 10% 10% - 20% > 20% Target Elements Copper and Iron. Antimony*, Cadmium, Lead, Nickel, Selenium, Silver, and Zinc. Arsenic, Chromium, and Mercury. Vanadium. * Calculation of RPDs versus sample spike concentrations rather than reference laboratory results (due to potential low bias in the reference laboratory results for antimony) decreases accuracy from Low to Very Low. Effects of Interferences: The RPDs from the evaluation of accuracy were further grouped and compared for a few elements of concern (arsenic, nickel, copper, and zinc) based on the relative concentrations of potentially interfering elements. Accuracy for copper was reduced from "moderate" (median RPDs less than 25 percent) to "very low" (median RPDs greater than 5 0 percent) by high relative concentrations of zinc (greater than 1 OX the arsenic concentration). Similarly, accuracy for nickel was reduced from "moderate" to "low" by high relative concentrations of copper. Low biases were produced in both the copper and nickel results by these interferences. Effects of Soil Characteristics: The RPDs from the evaluation of accuracy were also further evaluated in terms of sampling site and soil type. A slight prevalence of outliers was noted for some of the target elements in complex mining wastes from the Leviathan Mine, Torch Lake, Sulphur Bank Mine, Alton Steel, Wickes Smelter, and Ramsey Flats sample blends. However, the ranges of RPDs observed for the target elements were very broad and sample matrix appeared to have only a minor effect on these RPDs. Sample Throughput: The total processing time per sample was estimated at 12.2 minutes, which included 2.2 minutes of sample preparation and 9.5 minutes of instrument analysis time. On this basis, a sample throughput of A-3 ------- 49 samples per 8-hour work day was estimated. It is possible that sample throughput could be increased by using the autosampler accessory available from the developer. As noted above, however, the sample blends had undergone rigorous pre-processing before the demonstration. Sample throughput would have decreased if these processing steps (grinding, drying, sieving) had been performed during the demonstration; these steps can add from 10 minutes to 2 hours to the sample processing time. Costs: A cost assessment for the ElvaX identified a purchase cost of $35,000 as equipped for the demonstration. An autosampler ($20,000) and a helium purge unit ($10,000) are available as accessories. Using a hypothetical rental cost approximated from similar types of instruments, a total cost of $8,436 (with a labor cost of $5,901 at $43.75/hr) associated with sample preparation and analysis was estimated for a project similar to the demonstration (326 samples of soil and sediment). In comparison, the project cost averaged $8,932 for all eight XRF instruments participating in the demonstration, and $63,896 for fixed-laboratory analysis of all samples for the 13 target elements. Skills and Training Required: A degreed chemist is recommended, but not required, to operate the ElvaX. A second technician without specific training is also recommended to assist with sample preparation and data processing if the autosampler is not used. Xcalibur offers technical support and training through a telephone helpline and on an as needed basis. The operating software features helpful on-screen prompts for instrument operation. However, the abbreviated operating instructions available during the demonstration included no specific procedures to assist with the preparation and analysis of environmental samples. Health and Safety Aspects: The ElvaX's x-ray tube emits no detectable radiation thanks to two layers of lead shielding. The option of purging the sample chamber with helium requires the safe management of pressurized gas cylinders. Portability: Based on its dimensions (48 X 38 X 20 centimeters) and weight (18 kilograms), the ElvaX is a compact transportable instrument designed to be used on a table top or possibly a truck bed. The instrument and its laptop computer require 110 volt AC power. Durability: The ElvaX's x-ray tube has an expected lifespan of about 2 to 5 years of normal usage. The instrument is fully warranted for 1 year, and software is upgradeable for no cost. The instrument must be operated in a stable environment, free from excessive temperature and moisture extremes. Availability: The ElvaX is manufactured by Elvatech, Ltd., in Kiev, Ukraine. Xcalibur XRF Services, Inc., distributes and services the ElvaX from locations on the east and west coasts of the U.S., and in the Great Lakes region. The ElvaX is available for purchase and long-term leasing; no short-term rental options are currently available. RELATIVE PERFORMANCE The overall performance of the ElvaX relative to the average of all eight XRF instruments that participated in the demonstration is shown below: Sensitivity Accuracy Precision Antimony . . Arsenic 0 0 0 Cadmium ป Same 0 Chromium ป 0 0 Copper Same 0 Same Iron NC ป 0 Lead 0 0 0 Mercury Same 0 0 Nickel ป ป 0 Selenium 0 0 0 Silver 0 ป 0 Vanadium 0 0 0 Zinc Same 0 0 Key: Better Worse NC No MDL Calculated. NOTICE: Verifications are based on an evaluation of technology performance under specific, predetermined criteria and the appropriate quality assurance procedures. EPA makes no expressed or implied warranties as to the performance of the technology and does not certify that a technology will always operate as verified. The end user is solely responsible for complying with any and all applicable federal, state, and local requirements. ------- APPENDIX B DEVELOPER DISCUSSION ------- Developer Discussion - Xcalibur ElvaX XRF Analyzer 1. Portability The ElvaX offers compact size, low power consumption and can be connected to a DC to AC converter, making it useful as a portable EDXRF system. The ElvaX can be connected to a laptop computer via USB port and can be used in a truck bed or van for field measurement when heightened sensitivity or a longer measurement time is required. Although not available for this demonstration, the system can be equipped with an auto-sampler (carousel/changer) to allow greater measurement versatility. The optional auto-sampler does not add to the overall system size and only marginally adds to the weight. 2. Measurement Performance The ElvaX is capable of measurement without standards (Fundamental Parameters method); however, the results will be normalized to 100%. This means that the measurement results will be less accurate when less detectable elements are present. Using the dual filter and detection methods increases the detection of lower levels of elements in the lower end of the spectrum. The best results are obtained using a full range of standards. Our standards were limited to those soil samples used in the first stages of this study and the limited NIST standards available. Although Tetra Tech did an excellent job of providing prepared soil samples for this evaluation, optimum performance could have been achieved by further preparing the samples in pressed pellets. This would have added considerable time to sample preparation in exchange for better overall performance. The sample preparation we used was in keeping with the understood study concept of "field portability". The ElvaX has demonstrated excellent performance in measuring antimony, iron, nickel and chromium. Better results on other elements depend on the number of elements being measured simultaneously. Overlapping spectral peaks may pose a concern in certain situations where multiple elements are present (as in the case of arsenic and lead, where the lead La peak and arsenic Ka peaks overlap). This can be overcome by using alternate peaks if present (e.g., arsenic Kb at 11.7 kev and lead Lb at 12.6 kev); however, the detection limits may be higher. 3. Individual Element Comments Arsenic & Lead: For the calibration and detection, we used Ka for arsenic and La for lead. But with standards, we got very good de-convolution. Vanadium: The main problem in measuring vanadium was the overlapping Ti peaks which were not certified in the standards. As such it was not possible to calibrate the system for this element. Selenium: A few more standards programmed into the Product File (calibration) would be required for better performance results on this element. Overall performance can be enhanced with the addition of more standards for antimony, cadmium, and mercury. 4. Conclusion This was the first inclusion in the EPA SITE program for Xcalibur XRF Services and ElvaTech. Additional preparation and standards would dramatically increase the accuracy of measurements in this test. The ElvaX system will continue to evolve as a reliable, efficient, cost-effective tool for elemental analysis. B-l ------- APPENDIX C DATA VALIDATION SUMMARY REPORT ------- Contents Chapter Page Acronyms, Abbreviations, and Symbols ii 1.0 INTRODUCTION C-l 2.0 VALIDATION METHODOLOGY C-l 3.0 DATA VALIDATION C-3 3.1 Holding Time C-3 3.2 Calibration C-3 3.3 Laboratory Blanks C-4 3.4 Laboratory Control Samples C-5 3.5 Matrix Spike Samples C-5 3.6 Serial Dilution Results C-5 3.7 ICP Interference Check Samples C-6 3.8 Target Analyte Identification and Quantitation C-6 3.9 Quantitation Limit Verification C-6 4.0 PRECISION, ACCURACY, REPRESENTATIVENESS, COMPLETENESS, AND COMPARABILITY EVALUATION SUMMARY C-6 4.1 Precision C-7 4.2 Accuracy C-7 4.3 Representativeness C-7 4.4 Completeness C-7 4.5 Comparability C-7 5.0 CONCLUSIONS FOR DATA QUALITY AND DATA USABILITY C-8 6.0 REFERENCES C-8 APPENDIX DATA VALIDATION REPORTS ------- ABBREVIATIONS AND ACRONYMS CCV Continuing calibration verification CVAA Cold vapor atomic absorption DVSR Data validation summary report EPA U.S. Environmental Protection Agency FAR Federal acquisition regulations ICP-AES Inductively coupled plasma-atomic emission spectroscopy ICS Interference check sample ICV Initial calibration verification LCS Laboratory control sample LCSD Laboratory control sample duplicate MDL Method detection limit mg/kg Milligram per kilogram MS Matrix spike MSD Matrix spike duplicate PARCC Precision, accuracy, representativeness, completeness, and comparability PQL Practical quantitation limit QA/QC Quality assurance and quality control QAPP Quality assurance project plan QC Quality control RSD Relative standard deviation RPD Relative percent difference SDG Sample delivery group Shealy Shealy Environmental Services, Inc. SITE Superfund Innovative Technology Evaluation Tetra Tech Tetra Tech EM Inc. XRF X-ray fluorescence 11 ------- 1.0 INTRODUCTION This data validation summary report (DVSR) summarizes the reference laboratory quality control (QC) data gathered during the x-ray fluorescence (XRF) technologies demonstration conducted under the U.S. Environmental Protection Agency (EPA) Superfund Innovative Technology Evaluation (SITE) program. The reference laboratory was procured following the federal acquisition regulations (FAR) and an extensive selection process. Shealy Environmental Services, Inc. (Shealy), of Cayce, South Carolina, was selected as the reference laboratory for this project. Thirteen target analytes were measured in reference samples and include antimony, arsenic, cadmium, chromium, copper, iron, lead, mercury, nickel, selenium, silver, vanadium, and zinc. The laboratory reported results for 22 metals at the request of EPA; however, for the purposes of meeting project objectives, only the data validation for the 13 target analytes is summarized in this document. The objective of the validation is to determine the validity of the reference data, as well as its usability in meeting the primary objective of comparing reference data to XRF data generated during the demonstration. Shealy provided the data to Tetra Tech EM Inc. (Tetra Tech) in electronic and hardcopy formats; a total of 13 sample delivery groups (SDG) contain all the data for this project. The DVSR consists of seven sections, including this introduction. Section 2.0 presents the data validation methodology. Section 3.0 presents the results of the reference laboratory data validation. Section 4.0 summarizes the precision, accuracy, representativeness, completeness, and comparability (PARCC) evaluation. Section 5.0 presents conclusions about the overall evaluation of the reference data. Section 6.0 lists the references used to prepare this DVSR. Tables are presented following Section 6.0. 2.0 VALIDATION METHODOLOGY Data validation is the systematic process for reviewing and qualifying data against a set of criteria to ensure that the reference data are adequate for the intended use. The data validation process assesses acceptability of the data by evaluating the critical indicator parameters of PARCC. The laboratory analytical data were validated according to the procedures outlined in the following documents: "USEPA Contract Laboratory Program National Functional Guidelines for Inorganic Data Review" (EPA 2004), hereinafter referred to as the "EPA guidance." "Demonstration and Quality Assurance Project Plan, XRF Technologies for Measuring Trace Elements in Soil and Sediment" (Tetra Tech 2005), hereinafter referred to as "the QAPP." Data validation occurred in the following two stages: (1) a cursory review of analytical reports and quality assurance and quality control (QA/QC) information for 100 percent of the reference data and (2) full validation of analytical reports, QA/QC information, and associated raw data for 10 percent of the reference data as required by the QAPP (Tetra Tech 2005). QA/QC criteria were reviewed in accordance with EPA guidance (EPA 2004) and the QAPP (Tetra Tech 2005). The cursory review for total metals consisted of evaluating the following requirements, as applicable: Holding times C-l ------- Initial and continuing calibrations Laboratory blank results Laboratory control sample (LCS) and laboratory control sample duplicates (LCSD) results Matrix spike (MS) and matrix spike duplicate (MSB) results Serial dilutions results In addition to QA/QC criteria described above, the following criteria were reviewed during full validation: ICP interference check samples (ICS) Target analyte identification and quantitation Quantitation limit verification Section 3.0 presents the results of the both the cursory review and full validation. During data validation, worksheets were produced for each SDG that identify any QA/QC issues resulting in data qualification. Data validation findings were written in 13 individual data validation reports (one for each SDG). Data qualifiers were assigned to the results in the electronic database in accordance with EPA guidelines (EPA 2004). In addition to data validation qualifiers, comment codes were added to the database to indicate the primary reason for the validation qualifier. Table 1 defines data validation qualifiers and comment codes that are applied to the data set. Details about specific QC issues can be found in the individual SDG data validation reports and accompanying validation worksheets provided in the Appendix. The overall objective of data validation is to ensure that the quality of the reference data set is adequate for the intended use, as defined by the QAPP (Tetra Tech 2005) for the PARCC parameters. Table 2 provides the QC criteria as defined by the QAPP. PARCC parameters were assessed by completing the following tasks: Reviewing precision and accuracy of laboratory QC data Reviewing the overall analytical process, including holding time, calibration, analytical or matrix performance, and analyte identification and quantitation Assigning qualifiers to affected data when QA/QC criteria were not achieved Reviewing and summarizing implications of the frequency and severity of qualifiers in the validated data Prior to the XRF demonstration, soil and sediment samples were collected from nine locations across the U.S. and then blended, dried, sieved, and homogenized in the characterization laboratory to produce a set of 326 reference samples. Each of these samples were subsequently analyzed by both the reference C-2 ------- laboratory and all participating technology vendors. As such, 326 prepared soil/sediment samples were delivered to Shealy for the measurement of total metals. The analytical program included the following analyses and methods: Total metal for 22 analytes by inductively coupled plasma atomic emission spectroscopy (ICP-AES) according to EPA Methods 3050B/6010B (EPA 1996) Total mercury by cold vapor atomic absorption spectroscopy (CVAA) according to EPA Method 7471A (EPA 1996) 3.0 DATA VALIDATION RESULTS The parameters listed in Section 2.0 were evaluated during cursory review and full validation of analytical reports for all methods, as applicable. Each of the validation components discussed in this section is summarized as follows: Acceptable - All criteria were met and no data were qualified on that basis Acceptable with qualification - Most criteria were met, but at least one data point was qualified as estimated because of issues related to the review component Since no data were rejected, all data were determined to be either acceptable or acceptable with qualification. Sections 3.1 through 3.9 discuss each review component and the results of each. Tables that summarize the data validation findings follow Section 6.0 of this DVSR. Only qualified data are included in the tables. No reference laboratory data were rejected during the validation process. As such, all results are acceptable with the qualification noted in the sections that follow. 3.1 Holding Time Acceptable. The technical holding times were defined as the maximum time allowable between sample collection and, as applicable, sample extraction, preparation, or analysis. The holding times used for validation purposes were recommended in the specific analytical methods (EPA 1996) and were specified in the QAPP (Tetra Tech 2005). Because the soil and sediment samples were prepared prior to submission to the reference laboratory, and because the preparation included drying to remove moisture, no chemical or physical (for example ice) preservation was required. The holding time for sample digestion was 180 days for the ICP-AES analyses and 28 days for mercury. All sample digestions and analyses were conducted within the specified holding times. No data were qualified based on holding time exceedances. This fact contributes to the high technical quality of the reference data. 3.2 Calibration Acceptable. Laboratory instrument calibration requirements were established to ensure that analytical instruments could produce acceptable qualitative and quantitative data for all target analytes. Initial calibration demonstrates that the instrument is capable of acceptable performance at the beginning of an analytical run, while producing a linear curve. Continuing calibration demonstrates that the instrument is capable of repeating the performance established during the initial calibration (EPA 1996). C-3 ------- For total metal analyses (ICP-AES and CVAA), initial calibration review included evaluating criteria for the curve's correlation coefficient and initial calibration verification (ICV) percent recoveries. The ICV percent recoveries verify that the analytical system is operating within the established calibration criteria at the beginning of an analytical run. The continuing calibration review included evaluation of the criteria for continuing calibration verification (CCV) percent recoveries. The CCV percent recoveries verify that the analytical system is operating within the established calibration throughout the analytical run. All ICV and CCV percent recoveries associated with the reference data were within acceptable limits of 90 to 110 percent. As such, no data were qualified or rejected because of calibration exceedances. This fact contributes to the high technical quality of the data. 3.3 Laboratory Blanks Acceptable with qualification. No field blanks were required by the QAPP, since samples were prepared after collection and before submission to the reference laboratory. However, laboratory blanks were prepared and analyzed to evaluate the existence and magnitude of contamination resulting from laboratory activities. Blanks prepared and analyzed in the laboratory consisted of calibration and preparation blanks. If a problem with any blank existed, all associated data were carefully evaluated to assess whether the sample data were affected. At a minimum, calibration blanks were analyzed for every 10 analyses conducted on each instrument. Preparation blanks were prepared at a frequency of one per preparation batch per matrix or every 20 samples, whichever is greater (EPA 1996). When laboratory blank contamination was identified, sample results were compared to the practical quantitation limit (PQL) and the maximum blank value as required by the validation guidelines (EPA 2004). Most of the blank detections were positive results (i.e. greater than the method detection limit [MDL]), but less than the PQL. In these instances, if associated sample results were also less than the PQL, they were qualified as undetected (U); with the comment code "b." In these same instances, if the associated sample results were greater than the PQL, the reviewer used professional judgment to determine if the sample results were adversely affected. If so, then the results were qualified as estimated with the potential for being biased high (J+). If not, then no qualification was required. In a few cases, the maximum blank value exceeded the PQL. In these cases, all associated sample results less than the PQL were qualified as undetected (U) with the comment code "b." In cases where the associated sample results were greater than the PQL, but less than the blank concentration, the results were also qualified as undetected (U); with the comment code "b." If the associated sample results were greater than both the PQL and the blank value, the reviewer used professional judgment to determine if sample results were adversely affected. If so, then the results were qualified as estimated with the potential for being biased high (J+); with the comment code "b." Sample results significantly above the blank were not qualified. In addition to laboratory blank contamination, negative drift greater than the magnitude of the PQL was observed in some laboratory blanks. Associated sample data were qualified as undetected (U) if the results were less than the PQL. Professional judgement was used to determine if the negative drift adversely affected associated sample results greater than the PQL. If so, then sample results were qualified as estimated with the potential for being biased low (J-) due to the negative drift of the instrument baseline; with the comment code "b." Of all target analyte data, 2.6 percent of the data was qualified as undetected because of laboratory blank contamination (U, b), and less than 1 percent of the data was qualified as estimated (either J+, b or J-, b). The low occurrence of results affected by blank contamination indicates that the general quality of the C-4 ------- analytical data was not significantly compromised by blank contamination. Table 3 provides all results that were qualified based on laboratory blanks. 3.4 Laboratory Control Samples Acceptable. LCSs and LCSDs were prepared and analyzed with each batch of 20 or fewer samples of the same matrix. All percent recoveries were within the QC limits of 80 to 120 percent; all relative percent differences (RPD) between the LCD and LCSD values were less than the criterion of 20 percent. No data were qualified or rejected on the basis of LCS/LCSD results. This fact contributes to the high technical quality of the data. 3.5 Matrix Spike Samples Acceptable with qualification. MS and MSB samples were prepared and analyzed with each batch of 20 or fewer samples of the same matrix. All percent recoveries were within the QC limits of 75 to 125 percent, and all RPDs between the MS and MSB values were less than the criterion of 25 percent, except as discussed in the following paragraphs. Sample results affected by MS and MSB percent recoveries issues were qualified as estimated and either biased high (J+) if the recoveries were greater than 125 percent; or qualified as estimated and biased low (J-) if the recoveries were less than 75 percent. In at least one case, the MS was higher than 125 percent and the MSB was lower than 75 percent; the associated results were qualified as estimated (J) with no distinction for potential bias. All data qualified on the basis of MS and MSB recovery were also assigned the comment code "e." Of all target analyte data, less than 1 percent was qualified as estimated and biased high (J+, e), while about 8 percent of the data were qualified as estimated and biased low (J-, e). Antimony and silver were the most frequently qualified sample results. Based on experience, antimony and silver soil recoveries are frequently low using the selected methods. Table 4 provides the results that were qualified based on MS/MSB results. The precision between MS and MSB results were generally acceptable. If the RPB between MS and MSB results were greater than 25 percent, the data were already qualified based on exceedance of the acceptance window for recovery. Therefore, no additional qualification was required for MS/MSB precision. No data were rejected on the basis of MS/MSB results. The relatively low occurrence of data qualification due to MS/MSB recoveries and RPBs contribute to the high technical quality of the data. 3.6 Serial Dilution Results Acceptable with qualification. Serial dilutions were conducted and analyzed by Shealy at a frequency of 1 per batch of 20 samples. The serial dilution analysis can evaluate whether matrix interference exists and whether the accuracy of the analytical data is affected. For all target analyte data, less than 1 percent of the data was qualified as estimated and biased high (J+, j), while about 2 percent of the data were qualified as estimated and biased low (J-, j). Serial dilution results are used to determine whether characteristics of the digest matrix, such as viscosity or the presence of analytes at high concentrations, may interfere with the detected analytes. Qualifiers were applied to cases where interference was suspected. However, the low incidence of apparent matrix interference contributes to the high technical quality of the data. Table 5 provides the results that were qualified based on MS/MSB results. C-5 ------- 3.7 ICP Interference Check Samples Acceptable. ICP results for each ICS were evaluated. The ICS verifies the validity of the laboratory's inter-element and background correction factors. High levels of certain elements (including aluminum, calcium, iron, and magnesium) can affect sample results if the inter-element and background correction factors have not been optimized. Incorrect correction factors may result in false positives, false negatives, or biased results. All ICS recoveries were within QC limits of 80 to 120 percent, and no significant biases were observed due to potential spectral interference. No data were qualified or rejected because of ICS criteria violations. This fact contributes to the high technical quality of the data. 3.8 Target Analyte Identification and Quantitation Acceptable Identification is determined by measuring the characteristic wavelength of energy emitted by the analyte (ICP) or absorbed by the analyte (CVAA). External calibration standards are used to quantify the analyte concentration in the sample digest. Sample digest concentrations are converted to soil units (milligrams per kilogram) and corrected for percent moisture. For 10 percent of the samples, results were recalculated to verify the accuracy of reporting. All results were correctly calculated by the laboratory, except for one mercury result, whose miscalculation was the result of an error in entering the dilution factor. Shealy immediately resolved this error and corrected reports were provided. Since the result was corrected, no qualification was required. No other reporting errors were observed. For inorganic analyses, analytical instruments can make reliable qualitative identification of analytes at concentrations below the PQL. Detected results below the PQL are considered quantitatively uncertain. Sample results below the PQL were reported by the laboratory with a "J" qualifier. No additional qualification was required. 3.9 Quantitation Limit Verification Acceptable. Reference laboratory quantitation limits were specified in the QAPP (Tetra Tech 2005). Circumstances that affected quantitation were limited and included dilution and percent moisture factors. Since the samples were prepared prior to submission to the reference laboratory, moisture content was very low and had little impact on quantitation limits. The laboratory did correct all quantitation limits for moisture content. Due to the presence of percent-level analytes in some samples, dilutions were required. However, the required PQLs for the reference laboratory were high enough that even with dilution and moisture content factors applied, the reporting limits did not exceed those of the XRF instruments. This allows for effective comparison of results between the reference laboratory and XRF instruments. 4.0 PRECISION, ACCURACY, REPRESENTATIVENESS, COMPLETENESS, AND COMPARABILITY EVALUATION SUMMARY All analytical data were reviewed for PARCC parameters to validate reference data. The following sections discuss the overall data quality, including the PARCC parameters, as determined by the data validation. C-6 ------- 4.1 Precision Precision is a measure of the reproducibility of an experimental value without considering a true or referenced value. The primary indicators of precision were the MS/MSD RPD and LCS/LCSD RPD between the duplicate results. Precision criteria of less than 20 percent RPD for LCS/LCSD and 25 percent for MS/MSD were generally met for all duplicate pairs. No data were qualified based on duplicate precision of MS/MSD or LCS/LCSD pairs that were not already qualified for other reasons. Such low occurrence of laboratory precision problems supports the validity, usability, and defensibility of the data. 4.2 Accuracy Accuracy assesses the proximity of an experimental value to a true or referenced value. The primary accuracy indicators were the recoveries of MS and LCS spikes. Accuracy is expressed as percent recovery. Overall, about 8 percent of the data was qualified as estimated and no data were rejected because of accuracy problems. The low frequency of accuracy problems supports the validity, usability, and defensibility of the data. 4.3 Representativeness Representativeness refers to how well sample data accurately reflect true environmental conditions. The QAPP was carefully designed to ensure that actual environmental samples be collected by choosing representative sites across the US from which sample material was collected. The blending and homogenization was executed according to the approved QAPP (Tetra Tech 2005). 4.4 Completeness Completeness is defined as the percentage of measurements that are considered to be valid. The validity of sample results is evaluated through the data validation process. Sample results that are rejected and any missing analyses are considered incomplete. Data that are qualified as estimated (J) or undetected estimated (UJ) are considered valid and usable. Data qualified as rejected (R) are considered unusable for all purposes. Since no data were rejected in this data set, a completeness of 100 percent was achieved. A total of 4,238 target analyte results were evaluated. The completeness goal stated in the QAPP (Tetra Tech 2005) was 90 percent. 4.5 Comparability Comparability is a qualitative parameter that expresses the confidence with which one data set may be compared to another. Widely-accepted SW-846 methods were used for this project. It is recognized that direct comparison of the reference laboratory data (using ICP-AES and CVAA techniques) to the XRF measurements may result in discrepancies due to differences in the preparation and measurement techniques; however, the reference laboratory data is expected to provide an acceptable basis for comparison to XRF measurement results in accordance with the project objectives. Comparability of the data was also achieved by producing full data packages, by using a homogenous matrix, standard quantitation limits, standardized data validation procedures, and by evaluating the PARCC parameters uniformly. In addition, the use of specified and well-documented analyses, approved laboratories, and the standardized process of data review and validation have resulted in a high degree of comparability for the data. C-7 ------- 5.0 CONCLUSIONS FOR DATA QUALITY AND DATA USABILITY Although some qualifiers were added to the data, a final review of the data set with respect to the data quality parameters discussed in Section 4.0 indicates that the data are of overall good quality. No analytical data were rejected. The data quality is generally consistent with project objectives for producing data of suitable quality for comparison to XRF data. All supporting documentation and data are available upon request, including cursory review and full validation reports as well as the electronic database that contains sample results. 6.0 REFERENCES Tetra Tech EM, Inc. (Tetra Tech). 2005. "Demonstration and Quality Assurance Project Plan, XRF Technologies for Measuring Trace Elements in Soil and Sediment." March. U.S. Environmental Protection Agency (EPA). 1996. "Test Methods for Evaluating Solid Waste", Third Edition (SW-846). With promulgated revisions. December. EPA. 2004. "USEPA Contract Laboratory Program National Functional Guidelines For Inorganic Data Review". October. C-8 ------- TABLES C-9 ------- TABLE 1: DATA VALIDATION QUALIFIERS AND COMMENT CODES Qualifier No Qualifier U J J+ J- UJ R Comment Code a b c d e f g h i J Definition Indicates that the data are acceptable both qualitatively and quantitatively. Indicates compound was analyzed for but not detected above the concentration listed. The value listed is the sample quantitation limit. Indicates an estimated concentration value. The result is considered qualitatively acceptable, but quantitatively unreliable. The result is an estimated quantity, but the result may be biased high. The result is an estimated quantity, but the result may be biased low. Indicates an estimated quantitation limit. The compound was analyzed for, considered non-detected. The data are unusable (compound may or may not be present). Resampling reanalysis is necessary for verification. but was and Definition Surrogate recovery exceeded (not applicable to this data set) Laboratory method blank and common blank contamination Calibration criteria exceeded Duplicate precision criteria exceeded Matrix spike or laboratory control sample recovery exceeded Field blank contamination (not applicable to this data set) Quantification below reporting limit Holding time exceeded Internal standard criteria exceeded (not applicable to this data set) Other qualification (will be specified in report) C-9 ------- TABLE 2: QC CRITERIA Parameter Method QC Check Frequency Criterion Corrective Action Reference Method Target Metals ( 12 ICP metals andHg) Percent moisture 3 05 OB/601 OB and 7471 A Method and instrument blanks MS/MSD LCS/LCSD Performance audit samples Laboratory duplicates One per analytical batch of 20 or less One per analytical batch of 20 or less One per analytical batch of 20 or less One per analytical batch of 20 or less One per analytical batch of 20 or less Less than the reporting limit 75 to 125 percent recovery RPD<25 80 to 120 percent recovery RPD<20 Within acceptance limits RPD<20 1 . Check calculations 2. Assess and eliminate source of contamination 3 . Reanalyze blank 4. Inform Tetra Tech project manager 5. Flag affected results 1 . Check calculations 2. Check LCS/LCSD and digest duplicate results to determine whether they meet criterion 3 . Inform Tetra Tech project manager 4. Flag affected results 1 . Check calculations 2. Check instrument operating conditions and adjust as necessary 3 . Check MS/MSD and digest duplicate results to determine whether they meet criterion 4. Inform Tetra Tech project manager 5 . Redigest and reanalyze the entire batch of samples 6. Flag affected results 1 . Evaluated by Tetra Tech QA chemist 2. Inform laboratory and recommend changes 3 . Flag affected results 1 . Check calculations 2. Reanalyze sample batch 3 . Inform Tetra Tech project manager 4. Flag affected results C-10 ------- TABLE 3: DATA QUALIFICATION: LABORATORY METHOD BLANK CONTAMINATION Sample ID AS-SO-04-XX AS-SO-06-XX AS-SO-10-XX AS-SO-11-XX AS-SO-13-XX BN-SO-18-XX BN-SO-28-XX BN-SO-31-XX BN-SO-35-XX KP-SE-01-XX KP-SE-11-XX KP-SE-12-XX KP-SE-14-XX KP-SE-17-XX KP-SE-19-XX KP-SE-25-XX KP-SE-25-XX KP-SE-28-XX KP-SE-30-XX KP-SE-30-XX KP-SO-02-XX KP-SO-02-XX KP-SO-03-XX KP-SO-03-XX KP-SO-04-XX KP-SO-04-XX KP-SO-04-XX KP-SO-05-XX KP-SO-05-XX KP-SO-05-XX KP-SO-06-XX KP-SO-06-XX KP-SO-07-XX KP-SO-07-XX KP-SO-07-XX KP-SO-09-XX KP-SO-09-XX Analyte Selenium Antimony Selenium Selenium Antimony Silver Silver Silver Silver Mercury Mercury Mercury Mercury Mercury Mercury Mercury Selenium Mercury Mercury Selenium Mercury Selenium Cadmium Mercury Cadmium Mercury Selenium Cadmium Mercury Selenium Arsenic Mercury Arsenic Mercury Selenium Cadmium Mercury Result 6.2 2.4 1.1 1.1 2.4 0.94 0.77 0.97 0.85 0.053 0.079 0.06 0.065 0.082 0.044 0.096 0.26 0.056 0.1 0.24 0.043 0.42 0.074 0.044 0.046 0.018 0.28 0.13 0.044 0.24 0.73 0.059 2 0.027 0.21 0.094 0.046 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier U UJ U U UJ U U U U U U U U U U U U U U U U U U U U U U U U U J- u J- u U U U Comment Code b b,e b b b,e b b b b b b b b b b b b b b b b b b b b b b b b b b b b b b b b C-ll ------- TABLE 3: DATA QUALIFICATION: LABORATORY METHOD BLANK CONTAMINATION (Continued) Sample ID KP-SO-10-XX KP-SO-10-XX KP-SO-10-XX KP-SO-13-XX KP-SO-13-XX KP-SO-13-XX KP-SO-15-XX KP-SO-15-XX KP-SO-16-XX KP-SO-16-XX KP-SO-18-XX KP-SO-18-XX KP-SO-20-XX KP-SO-20-XX KP-SO-21-XX KP-SO-21-XX KP-SO-22-XX KP-SO-22-XX KP-SO-23-XX KP-SO-23-XX KP-SO-24-XX KP-SO-24-XX KP-SO-26-XX KP-SO-26-XX KP-SO-26-XX KP-SO-27-XX KP-SO-27-XX KP-SO-27-XX KP-SO-29-XX KP-SO-29-XX KP-SO-31-XX KP-SO-32-XX KP-SO-32-XX KP-SO-32-XX LV-SE-02-XX LV-SE-10-XX LV-SE-11-XX Analyte Arsenic Mercury Selenium Arsenic Cadmium Mercury Arsenic Mercury Cadmium Mercury Arsenic Mercury Arsenic Mercury Cadmium Mercury Arsenic Mercury Cadmium Mercury Arsenic Mercury Cadmium Mercury Selenium Arsenic Cadmium Mercury Arsenic Mercury Mercury Arsenic Cadmium Mercury Mercury Mercury Selenium Result 0.7 0.028 0.22 1.4 0.045 0.037 0.76 0.029 0.063 0.016 0.56 0.016 1.5 0.03 0.098 0.042 0.7 0.027 0.048 0.017 1.4 0.017 0.061 0.013 0.22 1.3 0.05 0.021 1.5 0.013 0.017 1.6 0.045 0.014 0.02 0.023 1.3 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier J- U U J- u U J- u U U J- u J- u U U J- u U U J- u U U U J- u U J- u U J- u U U U U Comment Code b b b b b b b b b b b b b b b b b b b b b b b b b b b b b b b b b b b b b C-12 ------- TABLE 3: DATA QUALIFICATION: LABORATORY METHOD BLANK CONTAMINATION (Continued) Sample ID LV-SE-14-XX LV-SE-21-XX LV-SE-24-XX LV-SE-29-XX LV-SE-32-XX RF-SE-07-XX RF-SE-08-XX RF-SE-10-XX RF-SE-12-XX RF-SE-23-XX RF-SE-23-XX RF-SE-33-XX RF-SE-36-XX RF-SE-36-XX RF-SE-45-XX RF-SE-53-XX SB-SO-03-XX SB-SO-12-XX SB-SO-13-XX SB-SO-15-XX SB-SO-17-XX SB-SO-18-XX SB-SO-30-XX SB-SO-32-XX SB-SO-37-XX SB-SO-46-XX SB-SO-48-XX SB-SO-53-XX TL-SE-01-XX TL-SE-03-XX TL-SE-03-XX TL-SE-04-XX TL-SE-10-XX TL-SE-11-XX TL-SE-12-XX TL-SE-14-XX TL-SE-15-XX Analyte Mercury Mercury Mercury Selenium Mercury Mercury Silver Silver Mercury Copper Zinc Silver Mercury Selenium Cadmium Cadmium Antimony Silver Silver Silver Silver Antimony Selenium Silver Silver Silver Silver Antimony Mercury Mercury Silver Mercury Mercury Mercury Mercury Mercury Mercury Result 0.056 0.048 0.053 1.2 0.052 0.091 0.39 0.34 0.099 0.2 0.6 0.33 0.081 1 0.52 0.57 1.2 2.1 2.2 1.6 2.3 1.2 1.3 0.1 2 2.2 0.1 1.2 0.074 0.32 0.94 0.26 0.19 0.021 0.22 0.08 0.28 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier U U U U U U U U U U U U U U U U UJ UJ UJ UJ UJ UJ J+ UJ UJ UJ UJ UJ U J- u J- J- u J- u J- Comment Code b b b b b b b b b b b b b b b b b,e b b b b,e b,e b b,e b b,e b,e b,e b b b b b b b b b C-13 ------- TABLE 3: DATA QUALIFICATION: LABORATORY METHOD BLANK CONTAMINATION (Continued) Sample ID TL-SE-15-XX TL-SE-18-XX TL-SE-19-XX TL-SE-19-XX TL-SE-20-XX TL-SE-22-XX TL-SE-23-XX TL-SE-23-XX TL-SE-24-XX TL-SE-24-XX TL-SE-25-XX TL-SE-25-XX TL-SE-26-XX TL-SE-27-XX TL-SE-29-XX TL-SE-31-XX TL-SE-31-XX WS-SO-06-XX WS-SO-08-XX WS-SO-10-XX WS-SO-12-XX WS-SO-17-XX WS-SO-20-XX WS-SO-23-XX WS-SO-30-XX WS-SO-31-XX WS-SO-35-XX Analyte Silver Mercury Mercury Silver Mercury Mercury Mercury Silver Mercury Silver Mercury Silver Mercury Mercury Mercury Mercury Silver Mercury Mercury Mercury Mercury Mercury Mercury Mercury Mercury Selenium Mercury Result 1 0.025 0.32 1.1 0.26 0.082 0.41 1.3 0.26 1.3 0.44 0.94 0.24 0.02 0.076 0.57 1.2 0.07 0.063 0.058 0.068 0.069 0.06 0.05 0.069 1.2 0.071 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier U U J- u J- u J- u J- u J- u J- u U J- u U U U UJ UJ U U UJ U UJ Comment Code b b b b b b b b b b b b b b b b b b b b b,e b,e b b b,e b b,e Notes: mg/kg b e J+ J- UJ Milligrams per kilogram Data were qualified based on blank contamination Data were additionally qualified based on matrix spike/matrix spike duplicate exceedances Result is estimated and potentially biased high Result is estimated and potentially biased low Result is undetected at estimated quantitation limits C-14 ------- TABLE 4: DATA QUALIFICATION: MATRIX SPIKE RECOVERY EXCEEDANCES Sample ID AS-SO-01-XX AS-SO-02-XX AS-SO-03-XX AS-SO-03-XX AS-SO-04-XX AS-SO-05-XX AS-SO-05-XX AS-SO-06-XX AS-SO-07-XX AS-SO-08-XX AS-SO-08-XX AS-SO-09-XX AS-SO-10-XX AS-SO-11-XX AS-SO-12-XX AS-SO-13-XX BN-SO-01-XX BN-SO-01-XX BN-SO-05-XX BN-SO-07-XX BN-SO-07-XX BN-SO-09-XX BN-SO-09-XX BN-SO-10-XX BN-SO-10-XX BN-SO-11-XX BN-SO-11-XX BN-SO-12-XX BN-SO-12-XX BN-SO-14-XX BN-SO-14-XX BN-SO-15-XX BN-SO-15-XX BN-SO-16-XX BN-SO-16-XX BN-SO-19-XX BN-SO-21-XX Analyte Antimony Antimony Mercury Silver Antimony Mercury Silver Antimony Antimony Mercury Silver Antimony Antimony Antimony Antimony Antimony Antimony Silver Antimony Antimony Silver Antimony Silver Antimony Silver Antimony Silver Antimony Silver Antimony Silver Antimony Silver Antimony Arsenic Antimony Antimony Result 3.8 <2.6 3.7 480 <6.4 2.5 330 2.4 3.6 2.5 280 <2.6 1.9 3.7 <2.6 2.4 <1.3 <1.3 160 110 990 750 100 <1.3 <1.3 4 140 750 210 3.5 140 <1.3 <1.3 120 1100 150 150 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier J- UJ J- J- UJ J- J- UJ J- J- J- UJ J- J- UJ UJ UJ UJ J- J- J+ J- J- UJ UJ J- J- J- J- J- J- UJ UJ J- J+ J- J- Validation Code e e e e e e e b,e e e e e e e e b,e e e e e e e e e e e e e e e e e e e e e e C-15 ------- TABLE 4: DATA QUALIFICATION: MATRIX SPIKE RECEOVERY EXCEEDANCES (Continued)) Sample ID BN-SO-21-XX BN-SO-23-XX BN-SO-23-XX BN-SO-24-XX BN-SO-24-XX BN-SO-25-XX BN-SO-25-XX BN-SO-26-XX BN-SO-29-XX BN-SO-32-XX BN-SO-33-XX CN-SO-01-XX CN-SO-02-XX CN-SO-03-XX CN-SO-04-XX CN-SO-05-XX CN-SO-06-XX CN-SO-07-XX CN-SO-08-XX CN-SO-09-XX CN-SO-10-XX CN-SO-11-XX KP-SE-01-XX KP-SE-01-XX KP-SE-08-XX KP-SE-08-XX KP-SE-11-XX KP-SE-11-XX KP-SE-12-XX KP-SE-12-XX KP-SE-14-XX KP-SE-14-XX KP-SE-17-XX KP-SE-17-XX KP-SE-25-XX KP-SE-25-XX KP-SE-30-XX Analyte Arsenic Antimony Silver Antimony Silver Antimony Arsenic Antimony Antimony Antimony Antimony Antimony Mercury Mercury Antimony Mercury Mercury Mercury Antimony Mercury Antimony Antimony Lead Silver Lead Silver Lead Silver Lead Silver Lead Silver Lead Silver Lead Silver Lead Result 1300 <1.2 130 810 140 82 700 150 150 160 100 13 270 34 13 280 40 36 15 260 13 17 310 <0.26 300 <0.27 310 <0.27 320 <0.26 680 <0.26 300 <0.27 310 <0.27 300 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier J+ UJ J- J- J- J- J J- J- J- J- J- J- J- J- J- J- J- J- J- J- J- J- UJ J- UJ J- UJ J- UJ J- UJ J- UJ J- UJ J- Validation Code e e e e e e,j e,j e e e e e e e e e e e e e e e e e e e e e e e e,j e e e e e e C-16 ------- TABLE 4: DATA QUALIFICATION: MATRIX SPIKE RECEOVERY EXCEEDANCES (Continued)) Sample ID KP-SE-30-XX KP-SO-04-XX KP-SO-06-XX KP-SO-07-XX KP-SO-10-XX KP-SO-13-XX KP-SO-15-XX KP-SO-16-XX KP-SO-18-XX KP-SO-20-XX KP-SO-22-XX KP-SO-23-XX KP-SO-24-XX KP-SO-26-XX KP-SO-27-XX KP-SO-29-XX KP-SO-32-XX LV-SE-01-XX LV-SE-02-XX LV-SE-02-XX LV-SE-02-XX LV-SE-05-XX LV-SE-06-XX LV-SE-07-XX LV-SE-08-XX LV-SE-09-XX LV-SE-10-XX LV-SE-10-XX LV-SE-10-XX LV-SE-11-XX LV-SE-12-XX LV-SE-13-XX LV-SE-14-XX LV-SE-15-XX LV-SE-15-XX LV-SE-16-XX LV-SE-17-XX Analyte Silver Antimony Antimony Antimony Antimony Antimony Antimony Antimony Antimony Antimony Antimony Antimony Antimony Antimony Antimony Antimony Antimony Antimony Antimony Lead Silver Mercury Mercury Antimony Antimony Lead Antimony Lead Silver Antimony Lead Mercury Antimony Antimony Silver Antimony Antimony Result <0.27 94 8.1 17 6.1 16 6.3 93 6.7 19 8.3 86 17 90 15 18 16 <1.5 <1.3 20 <1.3 2.6 610 <6.7 <1.3 14 <1.3 25 <1.3 <1.4 19 640 <1.5 290 300 <1.3 280 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier UJ J+ J+ J+ J+ J+ J+ J+ J+ J+ J+ J+ J+ J+ J+ J+ J+ UJ UJ J- UJ J- J- UJ UJ J- UJ J- UJ UJ J- J- UJ J+ J- UJ J+ Validation Code e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e C-17 ------- TABLE 4: DATA QUALIFICATION: MATRIX SPIKE RECEOVERY EXCEEDANCES (Continued)) Sample ID LV-SE-17-XX LV-SE-17-XX LV-SE-18-XX LV-SE-19-XX LV-SE-20-XX LV-SE-20-XX LV-SE-21-XX LV-SE-22-XX LV-SE-22-XX LV-SE-22-XX LV-SE-23-XX LV-SE-24-XX LV-SE-25-XX LV-SE-25-XX LV-SE-25-XX LV-SE-26-XX LV-SE-27-XX LV-SE-28-XX LV-SE-29-XX LV-SE-30-XX LV-SE-31-XX LV-SE-31-XX LV-SE-31-XX LV-SE-32-XX LV-SE-33-XX LV-SE-35-XX LV-SE-35-XX LV-SE-35-XX LV-SE-36-XX LV-SE-38-XX LV-SE-39-XX LV-SE-41-XX LV-SE-42-XX LV-SE-43-XX LV-SE-43-XX LV-SE-45-XX LV-SE-47-XX Analyte Lead Silver Antimony Lead Antimony Silver Antimony Antimony Lead Silver Antimony Antimony Antimony Lead Silver Lead Lead Antimony Antimony Antimony Antimony Lead Silver Antimony Lead Antimony Lead Silver Lead Lead Lead Mercury Lead Antimony Silver Antimony Antimony Result 17 200 <6.7 17 140 75 <1.5 <1.3 22 <1.3 <6.6 <1.5 <1.3 23 <1.3 25 16 <1.3 <1.4 <1.3 <1.3 49 <1.3 <1.4 21 <1.3 22 <1.3 21 15 22 610 22 160 60 <6.7 <1.3 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier J- J- UJ J- J+ J- UJ UJ J- UJ UJ UJ UJ J- UJ J- J- UJ UJ UJ UJ J- UJ UJ J- UJ J- UJ J- J- J- J- J- J+ J- UJ UJ Validation Code e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e C-18 ------- TABLE 4: DATA QUALIFICATION: MATRIX SPIKE RECEOVERY EXCEEDANCES (Continued)) Sample ID LV-SE-48-XX LV-SE-50-XX LV-SE-51-XX LV-SE-51-XX LV-SO-03-XX LV-SO-03-XX LV-SO-04-XX LV-SO-04-XX LV-SO-34-XX LV-SO-34-XX LV-SO-37-XX LV-SO-40-XX LV-SO-40-XX LV-SO-49-XX LV-SO-49-XX RF-SE-02-XX RF-SE-03-XX RF-SE-04-XX RF-SE-04-XX RF-SE-05-XX RF-SE-05-XX RF-SE-06-XX RF-SE-13-XX RF-SE-14-XX RF-SE-14-XX RF-SE-15-XX RF-SE-19-XX RF-SE-19-XX RF-SE-22-XX RF-SE-24-XX RF-SE-25-XX RF-SE-26-XX RF-SE-26-XX RF-SE-27-XX RF-SE-28-XX RF-SE-30-XX RF-SE-31-XX Analyte Antimony Lead Antimony Silver Mercury Silver Mercury Silver Mercury Silver Mercury Mercury Silver Mercury Silver Antimony Antimony Antimony Silver Antimony Silver Antimony Antimony Antimony Silver Antimony Antimony Silver Antimony Antimony Antimony Antimony Silver Antimony Antimony Antimony Antimony Result <6.6 24 210 250 48 210 130 <1.2 130 <1.2 130 46 210 52 220 <1.3 <1.2 3.2 12 4.1 7.4 <1.3 <1.3 4.4 13 <1.3 3.7 14 <1.3 <1.3 <1.3 2.2 7.2 <1.3 <1.2 <1.3 <1.3 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier UJ J- J+ J- J- J- J- UJ J- UJ J- J- J- J- J- UJ UJ J+ J- J+ J- UJ UJ J+ J- UJ J+ J- UJ UJ UJ J+ J- UJ UJ UJ UJ Validation Code e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e e C-19 ------- TABLE 4: DATA QUALIFICATION: MATRIX SPIKE RECEOVERY EXCEEDANCES (Continued)) Sample ID RF-SE-32-XX RF-SE-34-XX RF-SE-34-XX RF-SE-38-XX RF-SE-39-XX RF-SE-39-XX RF-SE-42-XX RF-SE-43-XX RF-SE-44-XX RF-SE-44-XX RF-SE-45-XX RF-SE-49-XX RF-SE-52-XX RF-SE-52-XX RF-SE-53-XX RF-SE-55-XX RF-SE-56-XX RF-SE-56-XX RF-SE-57-XX RF-SE-58-XX RF-SE-59-XX SB-SO-01-XX SB-SO-02-XX SB-SO-02-XX SB-SO-03-XX SB-SO-04-XX SB-SO-05-XX SB-SO-06-XX SB-SO-07-XX SB-SO-08-XX SB-SO-09-XX SB-SO-09-XX SB-SO-10-XX SB-SO-11-XX SB-SO-12-XX SB-SO-13-XX SB-SO-14-XX Analyte Antimony Antimony Silver Antimony Antimony Silver Antimony Antimony Antimony Silver Antimony Antimony Antimony Silver Antimony Antimony Antimony Silver Antimony Antimony Antimony Antimony Antimony Silver Antimony Silver Antimony Antimony Antimony Antimony Antimony Silver Antimony Antimony Antimony Antimony Antimony Result <1.3 2.9 10 <1.2 2.9 8.2 <1.3 <1.3 2.7 7.2 <1.3 <1.2 3.4 11 <1.3 <1.2 3.5 8.3 <1.3 <1.3 <1.3 180 44 <1.2 1.2 <1.3 1.6 1.7 45 5.4 <1.3 160 62 5.7 620 430 4.1 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier UJ J+ J- UJ J+ J- UJ UJ J+ J- UJ UJ J+ J- UJ UJ J+ J- UJ UJ UJ J J- UJ UJ UJ J- J- J J- UJ J- J J- J J J- Validation Code e e e e e e e e e e e e e e e e e e e e e e e,j e b, e e e e e e e e e e e e e C-20 ------- TABLE 4: DATA QUALIFICATION: MATRIX SPIKE RECEOVERY EXCEEDANCES (Continued)) Sample ID SB-SO-15-XX SB-SO-16-XX SB-SO-17-XX SB-SO-17-XX SB-SO-18-XX SB-SO-19-XX SB-SO-20-XX SB-SO-20-XX SB-SO-21-XX SB-SO-22-XX SB-SO-23-XX SB-SO-23-XX SB-SO-24-XX SB-SO-25-XX SB-SO-26-XX SB-SO-27-XX SB-SO-28-XX SB-SO-28-XX SB-SO-29-XX SB-SO-30-XX SB-SO-31-XX SB-SO-31-XX SB-SO-32-XX SB-SO-32-XX SB-SO-33-XX SB-SO-33-XX SB-SO-34-XX SB-SO-35-XX SB-SO-36-XX SB-SO-37-XX SB-SO-38-XX SB-SO-39-XX SB-SO-40-XX SB-SO-41-XX SB-SO-42-XX SB-SO-43-XX SB-SO-43-XX Analyte Antimony Antimony Antimony Silver Antimony Antimony Antimony Silver Antimony Antimony Antimony Silver Antimony Antimony Antimony Antimony Antimony Silver Silver Antimony Antimony Silver Antimony Silver Antimony Silver Silver Antimony Silver Antimony Antimony Antimony Antimony Antimony Antimony Antimony Silver Result 600 170 800 2.3 1.2 310 <1.3 140 4.9 10 48 <0.26 180 6.8 61 6.7 42 <0.26 <1.2 3.2 <1.3 160 46 0.1 350 2 <1.3 6 <1.2 340 <1.3 4.7 2.2 <1.3 4.6 40 <0.26 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier J- J J+ UJ UJ J UJ J- J J J- UJ J J+ J J+ J- UJ UJ J- UJ J- J- UJ J J UJ J+ UJ J UJ J- J- UJ J- J- UJ Validation Code i,e e e b,e b, e e e e e ej e e e e e e e e e e e ej e b,e e e e e e e e e e e e e e C-21 ------- TABLE 4: DATA QUALIFICATION: MATRIX SPIKE RECEOVERY EXCEEDANCES (Continued)) Sample ID SB-SO-44-XX SB-SO-45-XX SB-SO-45-XX SB-SO-46-XX SB-SO-46-XX SB-SO-47-XX SB-SO-48-XX SB-SO-48-XX SB-SO-49-XX SB-SO-50-XX SB-SO-51-XX SB-SO-52-XX SB-SO-53-XX SB-SO-54-XX SB-SO-54-XX SB-SO-55-XX SB-SO-55-XX SB-SO-56-XX TL-SE-01-XX TL-SE-01-XX TL-SE-01-XX TL-SE-05-XX TL-SE-05-XX TL-SE-09-XX TL-SE-09-XX TL-SE-11-XX TL-SE-11-XX TL-SE-11-XX TL-SE-13-XX TL-SE-13-XX TL-SE-14-XX TL-SE-14-XX TL-SE-14-XX TL-SE-18-XX TL-SE-18-XX TL-SE-18-XX TL-SE-22-XX Analyte Antimony Antimony Silver Antimony Silver Antimony Antimony Silver Silver Antimony Antimony Antimony Antimony Lead Silver Antimony Silver Silver Antimony Lead Silver Antimony Silver Antimony Silver Antimony Lead Silver Antimony Silver Antimony Lead Silver Antimony Lead Silver Antimony Result 6.8 180 2.1 740 2.2 <1.3 39 0.1 <1.2 57 <1.3 150 1.2 5.2 <0.5 340 2.2 <1.2 <1.2 48 5.7 100 180 100 170 <1.2 54 5.5 95 160 <1.2 50 5.7 <1.2 46 6.3 <1.2 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier J+ J J- J+ UJ UJ J- UJ UJ J UJ J UJ J- UJ J J UJ UJ J- J- J+ J- J+ J- UJ J- J- J+ J UJ J- J- UJ J- J- UJ Validation Code e e e e b, e e e b, e e e e e b,e e e e e e e e e e e e e e e e j,e j,e e e e e e e e C-22 ------- TABLE 4: DATA QUALIFICATION: MATRIX SPIKE RECEOVERY EXCEEDANCES (Continued)) Sample ID TL-SE-22-XX TL-SE-22-XX TL-SE-27-XX TL-SE-27-XX TL-SE-27-XX TL-SE-29-XX TL-SE-29-XX TL-SE-29-XX WS-SO-01-XX WS-SO-01-XX WS-SO-01-XX WS-SO-02-XX WS-SO-02-XX WS-SO-03-XX WS-SO-03-XX WS-SO-04-XX WS-SO-04-XX WS-SO-05-XX WS-SO-05-XX WS-SO-07-XX WS-SO-09-XX WS-SO-09-XX WS-SO-10-XX WS-SO-11-XX WS-SO-12-XX WS-SO-12-XX WS-SO-13-XX WS-SO-13-XX WS-SO-14-XX WS-SO-14-XX WS-SO-15-XX WS-SO-15-XX WS-SO-16-XX WS-SO-16-XX WS-SO-17-XX WS-SO-17-XX WS-SO-18-XX Analyte Lead Silver Antimony Lead Silver Antimony Lead Silver Antimony Mercury Silver Antimony Silver Antimony Mercury Antimony Silver Antimony Silver Silver Antimony Mercury Silver Silver Antimony Mercury Antimony Silver Antimony Mercury Antimony Silver Antimony Silver Antimony Mercury Antimony Result 54 6.5 <1.2 51 7.8 <1.2 51 5.9 41 5.8 69 130 150 8.9 0.86 45 76 8.6 0.76 400 7.1 0.89 <1.3 340 <1.3 0.068 200 170 8.4 0.74 48 90 110 150 <1.3 0.069 130 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier J- J- UJ J- J- UJ J- J- J- J J- J- J- J- J- J- J- J- J- J- J- J- UJ J- UJ UJ J- J- J- J- J- J- J- J- UJ UJ J- Validation Code e e e e e e e e e ej e e e e e e e e e e e e e e e b, e e e e e e e e e e b, e e C-23 ------- TABLE 4: DATA QUALIFICATION: MATRIX SPIKE RECEOVERY EXCEEDANCES (Continued)) Sample ID WS-SO-18-XX WS-SO-19-XX WS-SO-19-XX WS-SO-20-XX WS-SO-21-XX WS-SO-21-XX WS-SO-22-XX WS-SO-22-XX WS-SO-23-XX WS-SO-24-XX WS-SO-24-XX WS-SO-25-XX WS-SO-26-XX WS-SO-26-XX WS-SO-27-XX WS-SO-27-XX WS-SO-28-XX WS-SO-28-XX WS-SO-29-XX WS-SO-29-XX WS-SO-30-XX WS-SO-30-XX WS-SO-31-XX WS-SO-31-XX WS-SO-32-XX WS-SO-32-XX WS-SO-33-XX WS-SO-33-XX WS-SO-34-XX WS-SO-34-XX WS-SO-35-XX WS-SO-35-XX WS-SO-36-XX WS-SO-36-XX WS-SO-37-XX WS-SO-37-XX Analyte Silver Antimony Silver Silver Antimony Silver Antimony Silver Silver Antimony Silver Silver Antimony Mercury Antimony Mercury Antimony Silver Antimony Silver Antimony Mercury Antimony Mercury Antimony Silver Antimony Mercury Antimony Silver Antimony Mercury Antimony Silver Antimony Silver Result 140 150 160 <1.3 120 150 41 72 <1.3 97 140 450 7.6 0.83 <1.3 0.11 120 130 120 140 1.2 0.069 7.2 0.85 190 190 6.9 0.87 45 78 <1.3 0.071 120 120 120 140 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier J- J- J- UJ J- J- J- J- UJ J- J- J- J- J- UJ J- J- J- J- J- J- UJ J- J- J- J- J- J- J- J- UJ UJ J- J- J- J- Validation Code e e e e e e e e e e e e e e e e e e e e e b, e e e e e e e e e e b, e e e e e C-24 ------- TABLE 4: DATA QUALIFICATION: MATRIX SPIKE RECEOVERY EXCEEDANCES (Continued)) Notes: < = Less than mg/kg = Milligram per kilogram b = Data were qualified based on blank contamination e = Data were additionally qualified based on matrix spike/matrix spike duplicate exceedances j = Data were additionally qualified based on serial dilution exceedances J = Result is estimated and biased could not be determined J+ = Result is estimated and potentially biased high J- = Result is estimated and potentially biased low UJ = Result is undetected at estimated quantitation limit C-25 ------- TABLE 5: DATA QUALIFICATION: SERIAL DILUTION EXCEEDANCES Sample ID AS-SO-09-XX AS-SO-09-XX AS-SO-09-XX AS-SO-09-XX AS-SO-09-XX AS-SO-09-XX AS-SO-09-XX AS-SO-09-XX AS-SO-09-XX AS-SO-09-XX BN-SO-11-XX BN-SO-25-XX BN-SO-25-XX BN-SO-25-XX BN-SO-25-XX BN-SO-25-XX BN-SO-25-XX BN-SO-25-XX BN-SO-25-XX BN-SO-25-XX BN-SO-25-XX BN-SO-25-XX BN-SO-25-XX KP-SE-14-XX KP-SE-14-XX KP-SE-14-XX KP-SE-14-XX KP-SE-14-XX KP-SE-14-XX LV-SE-29-XX LV-SE-29-XX LV-SE-35-XX LV-SE-35-XX LV-SE-35-XX LV-SE-35-XX LV-SE-35-XX LV-SE-35-XX LV-SO-34-XX Analyte Arsenic Cadmium Chromium Copper Iron Lead Nickel Silver Vanadium Zinc Mercury Antimony Arsenic Cadmium Chromium Copper Iron Lead Nickel Selenium Silver Vanadium Zinc Antimony Chromium Copper Iron Lead Nickel Lead Mercury Arsenic Chromium Iron Nickel Vanadium Zinc Antimony Result 25 100 390 250 94000 3200 170 9.6 65 6800 24 82 700 370 64 930 16000 5400 88 19 48 28 2900 11 46 2.7 520 680 23 7.2 1.5 31 74 24000 170 55 67 870 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier J- J- J- J- J- J- J- J- J- J- J- J- J J- J- J- J- J- J- J- J- J- J- J- J- J+ J- J- J- J+ J- J- J- J- J- J- J- J- Comment Code j j j j j j i j j j j e,i ej j j j j j i j j j j i j j j ej j j i j j j j i j j C-26 ------- TABLE 5: DATA QUALIFICATION: SERIAL DILUTION EXCEEDANCES (Continued)) Sample ID LV-SO-34-XX LV-SO-34-XX LV-SO-34-XX LV-SO-34-XX LV-SO-34-XX LV-SO-34-XX LV-SO-34-XX LV-SO-34-XX LV-SO-34-XX RF-SE-16-XX RF-SE-16-XX RF-SE-16-XX RF-SE-16-XX RF-SE-16-XX RF-SE-16-XX RF-SE-16-XX RF-SE-16-XX RF-SE-16-XX RF-SE-16-XX RF-SE-16-XX RF-SE-24-XX RF-SE-24-XX RF-SE-24-XX RF-SE-24-XX RF-SE-24-XX RF-SE-24-XX RF-SE-24-XX RF-SE-24-XX RF-SE-24-XX RF-SE-24-XX SB-SO-02-XX SB-SO-02-XX SB-SO-02-XX SB-SO-02-XX SB-SO-15-XX SB-SO-15-XX SB-SO-15-XX SB-SO-15-XX Analyte Arsenic Cadmium Chromium Iron Lead Nickel Selenium Vanadium Zinc Antimony Arsenic Cadmium Chromium Copper Iron Lead Nickel Silver Vanadium Zinc Arsenic Cadmium Chromium Copper Iron Lead Nickel Silver Vanadium Zinc Antimony Arsenic Lead Mercury Antimony Arsenic Chromium Copper Result 110 2300 2200 20000 3700 1900 220 230 48 85 72 310 820 73 16000 24 1700 130 32 760 130 6.5 74 860 24000 410 170 3.8 46 1400 44 23 22 130 600 170 91 30 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier J- J- J- J- J- J- J- J- J- J- J- J- J- J- J- J- J- J- J- J- J+ J+ J+ J+ J+ J+ J+ J+ J+ J- J- J- J- J+ J- J- J- J- Comment Code j j j j i j j j j j j i j j j j i j j j j j j i j j j j i j ej j j j j,e i j j C-27 ------- TABLE 5: DATA QUALIFICATION: SERIAL DILUTION EXCEEDANCES (Continued)) Sample ID SB-SO-15-XX SB-SO-15-XX SB-SO-15-XX SB-SO-15-XX SB-SO-15-XX SB-SO-22-XX SB-SO-22-XX SB-SO-31-XX SB-SO-31-XX SB-SO-31-XX SB-SO-31-XX SB-SO-31-XX TL-SE-13-XX TL-SE-13-XX TL-SE-13-XX TL-SE-13-XX TL-SE-13-XX TL-SE-13-XX TL-SE-13-XX WS-SO-01-XX WS-SO-33-XX WS-SO-33-XX WS-SO-33-XX WS-SO-33-XX WS-SO-33-XX WS-SO-33-XX WS-SO-33-XX WS-SO-33-XX WS-SO-33-XX WS-SO-33-XX Analyte Iron Lead Nickel Vanadium Zinc Antimony Zinc Arsenic Nickel Selenium Silver Zinc Antimony Chromium Copper Iron Lead Silver Vanadium Mercury Arsenic Cadmium Chromium Copper Iron Lead Nickel Silver Vanadium Zinc Result 51000 40 100 52 36 10 64 8 3200 28 160 3900 95 36 4400 22000 1100 160 59 5.8 450 11 120 150 28000 3700 65 13 53 830 Unit mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Qualifier J- J- J- J- J- J J- J- J- J- J- J- J+ J+ J+ J+ J+ J J+ J J- J- J- J- J- J- J- J- J- J- Comment Code J J J J i ej J J J J e,j i j,e J J J i j,e J e,j J J J i J J J J i J Notes: mg/kg e J J J+ J- Milligram per kilogram Data were additionally qualified based on matrix spike/matrix spike duplicate exceedances Data were qualified based on serial dilution exceedances Result is estimated and biased could not be determined Result is estimated and potentially biased high Result is estimated and potentially biased low C-28 ------- APPENDIX D DEVELOPER AND REFERENCE LABORATORY DATA ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory Blend No. i i i i i i i i i i 2 2 2 2 2 2 2 2 2 2 2 2 2 2 3 3 3 3 3 3 3 3 3 3 Sample ID KP-SO-06-XX KP-SO-10-XX KP-SO-15-XX KP-SO-18-XX KP-SO-22-XX KP-SO-06-XC KP-SO-10-XC KP-SO-15-XC KP-SO-18-XC KP-SO-22-XC KP-SO-07-XX KP-SO-13-XX KP-SO-20-XX KP-SO-24-XX KP-SO-27-XX KP-SO-29-XX KP-SO-32-XX KP-SO-07-XC KP-SO-13-XC KP-SO-20-XC KP-SO-24-XC KP-SO-27-XC KP-SO-29-XC KP-SO-32-XC KP-SO-04-XX KP-SO-16-XX KP-SO-23-XX KP-SO-26-XX KP-SO-31-XX KP-SO-04-XC KP-SO-16-XC KP-SO-23-XC KP-SO-26-XC KP-SO-31-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 8.1 J+ 6.1 J+ 6.3 J+ 6.7 J+ 8.3 J+ 8 12 6 8 6 17 J+ 16 J+ 19 J+ 17 J+ 15 J+ 18 J+ 16 J+ 16 14 20 21 23 14 21 94 J+ 93 J+ 86 J+ 90 J+ 88 71 80 82 74 As i j- i j- i j- i j- i j- 68 111 84 76 57 2 J- 1 J- 2 J- 1 J- 1 J- 2 J- 2 J- 83 98 73 85 43 44 0 3 3 3 4 28 176 70 77 63 0 Cd 0.1 U 0.1 U 0.1 U 0.1 U 0.1 U 25 23 0.1 U 0.045 U 0.1 U 0.1 U 0.05 U 0.1 U 0.045 U 26 26 30 0.046 U 0.063 U 0.048 U 0.061 U 0.1 U 36 62 82 24 Cr 290 300 340 250 260 306 323 298 277 326 170 180 160 160 170 150 180 198 219 193 205 182 217 216 180 200 180 210 140 163 168 185 171 146 Cu 26 26 26 24 29 17 14 16 22 16 48 52 46 49 45 42 50 39 39 35 33 43 37 40 200 230 190 230 200 172 149 183 176 156 Fe 1,400 1,600 1,600 1,200 1,300 1,292 1,287 1,407 1,206 1,389 990 980 910 900 970 870 970 906 1,001 933 930 922 964 914 1,300 1,400 1,300 1,500 1,100 1,057 981 1,079 1,088 903 Pb 620 560 510 500 650 478 527 541 518 551 1,200 1,200 1,300 1,100 1,200 1,200 1,200 1,192 1,248 1,156 1,150 1,252 1,279 1,168 5,800 6,100 5,300 6,500 5,700 5,603 5,618 5,944 6,142 5,458 Hg 0.059 U 0.028 U 0.029 U 0.016 U 0.027 U 2 0.027 U 0.037 U 0.03 U 0.017 U 0.021 U 0.013 U 0.014 U 3 0.018 U 0.016 U 0.017 U 0.013 U 0.017 U 5 3 3 5 D-l ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. i i i i i i i i i i 2 2 2 2 2 2 2 2 2 2 2 2 2 2 3 3 3 3 3 3 3 3 3 3 Sample ID KP-SO-06-XX KP-SO-10-XX KP-SO-15-XX KP-SO-18-XX KP-SO-22-XX KP-SO-06-XC KP-SO-10-XC KP-SO-15-XC KP-SO-18-XC KP-SO-22-XC KP-SO-07-XX KP-SO-13-XX KP-SO-20-XX KP-SO-24-XX KP-SO-27-XX KP-SO-29-XX KP-SO-32-XX KP-SO-07-XC KP-SO-13-XC KP-SO-20-XC KP-SO-24-XC KP-SO-27-XC KP-SO-29-XC KP-SO-32-XC KP-SO-04-XX KP-SO-16-XX KP-SO-23-XX KP-SO-26-XX KP-SO-31-XX KP-SO-04-XC KP-SO-16-XC KP-SO-23-XC KP-SO-26-XC KP-SO-31-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 140 150 170 120 130 138 144 160 138 141 87 90 79 78 87 73 88 93 92 86 87 107 95 83 93 100 91 110 68 77 70 101 87 74 Se 0.25 U 0.22 U 0.25 U 0.25 U 0.25 U 38 14 0.21 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.51 11 35 23 50 0.28 U 0.25 U 0.25 U 0.22 U 0.25 U 25 6 54 59 51 Ag 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 13 14 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 13 4 5 3 12 6 0.16 J 0.16 J 0.13 J 0.17 J 0.4 11 20 4 12 V 2 J 2 J 2 J 2 J 2 J 0 0 0 0 0 1 J 1 J 1 J 1 J 1 J 1 J 1 J 0 0 0 0 0 0 0 1 J 1 J 1 J 1 J 2 J 34 0 0 0 0 Zn 11 12 15 11 11 41 0 33 21 37 26 24 25 22 24 22 24 67 75 56 60 78 55 60 45 47 41 52 38 82 80 79 94 68 D-2 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 4 4 4 4 4 4 4 4 4 4 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Sample ID KP-SO-02-XX KP-SO-03-XX KP-SO-05-XX KP-SO-09-XX KP-SO-21-XX KP-SO-02-XC KP-SO-03-XC KP-SO-05-XC KP-SO-09-XC KP-SO-21-XC WS-SO-06-XX WS-SO-08-XX WS-SO-12-XX WS-SO-17-XX WS-SO-27-XX WS-SO-30-XX WS-SO-35-XX WS-SO-06-XC WS-SO-08-XC WS-SO-12-XC WS-SO-17-XC WS-SO-27-XC WS-SO-30-XC WS-SO-35-XC WS-SO-03-XX WS-SO-05-XX WS-SO-09-XX WS-SO-14-XX WS-SO-26-XX WS-SO-31-XX WS-SO-33-XX WS-SO-03-XC WS-SO-05-XC WS-SO-09-XC WS-SO-14-XC WS-SO-26-XC WS-SO-31-XC WS-SO-33-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 410 360 410 420 370 233 242 237 240 252 1.3 U 1.3 1.3 UJ 1.3 UJ 1.3 UJ 1.2 J- 1.3 UJ 1 1 1 1 3 1 1 8.9 J- 8.6 J- 7.1 J- 8.4 J- 7.6 J- 7.2 J- 6.9 J- 36 41 38 39 23 26 25 As 10 9 12 11 10 0 94 0 49 86 48 45 43 47 49 51 49 105 108 113 102 81 60 94 500 440 480 430 520 520 450 J- 473 537 490 427 297 252 195 Cd 0.1 0.074 U 0.13 U 0.094 U 0.098 U 32 1.9 2 1.8 1.9 2 2 2 31 25 41 30 12 12 12 11 12 12 11 J- 34 10 12 36 28 Cr 6 5 6 5 5 120 120 110 120 120 130 130 61 79 59 49 64 39 140 140 130 120 140 140 120 J- 52 56 72 64 51 45 Cu 780 670 780 780 700 614 641 609 641 666 50 47 45 49 51 53 51 68 73 69 70 61 56 61 170 160 160 150 160 170 150 J- 199 187 195 182 150 158 165 Fe 1,700 1,600 2,000 1,800 1,700 1,047 1,084 1,130 1,070 1,167 28,000 26,000 25,000 28,000 28,000 29,000 28,000 21,856 21,786 21,623 21,219 18,393 19,246 19,086 32,000 31,000 30,000 28,000 30,000 32,000 28,000 J- 23,201 23,725 23,021 22,896 19,241 19,974 20,042 Pb 18,000 19,000 24,000 22,000 19,000 18,603 19,642 19,166 19,206 20,448 110 71 65 70 72 81 74 202 180 164 181 172 149 152 4,300 4,000 4,000 3,700 4,000 4,200 3,700 J- 9,334 9,860 9,696 9,433 6,110 7,009 6,809 Hg 0.043 U 0.044 U 0.044 U 0.046 U 0.042 U 15 12 12 11 13 0.07 U 0.063 U 0.068 UJ 0.069 UJ 0.11 J- 0.069 UJ 0.071 UJ 3 5 0.86 J- 0.76 J- 0.89 J- 0.74 J- 0.83 J- 0.85 J- 0.87 J- 7 27 9 D-3 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 4 4 4 4 4 4 4 4 4 4 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Sample ID KP-SO-02-XX KP-SO-03-XX KP-SO-05-XX KP-SO-09-XX KP-SO-21-XX KP-SO-02-XC KP-SO-03-XC KP-SO-05-XC KP-SO-09-XC KP-SO-21-XC WS-SO-06-XX WS-SO-08-XX WS-SO-12-XX WS-SO-17-XX WS-SO-27-XX WS-SO-30-XX WS-SO-35-XX WS-SO-06-XC WS-SO-08-XC WS-SO-12-XC WS-SO-17-XC WS-SO-27-XC WS-SO-30-XC WS-SO-35-XC WS-SO-03-XX WS-SO-05-XX WS-SO-09-XX WS-SO-14-XX WS-SO-26-XX WS-SO-31-XX WS-SO-33-XX WS-SO-03-XC WS-SO-05-XC WS-SO-09-XC WS-SO-14-XC WS-SO-26-XC WS-SO-31-XC WS-SO-33-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 4 3 4 3 4 2 2 3 2 3 61 58 55 59 61 65 62 39 57 39 38 55 35 70 75 71 70 64 70 72 65 J- 71 58 55 67 60 35 67 Se 0.42 U 0.25 U 0.24 U 0.25 U 0.25 U 275 230 231 240 211 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 34 15 5 1.6 1.3 U 1.3 U 1.3 U 1.3 U 1.2 U 1.3 U 43 19 16 Ag 0.82 0.73 0.82 0.84 0.76 42 31 13 25 27 0.93 J 0.86 J 0.94 J 0.89 J 0.9 J 1 J 1 J 10 11 10 10 6 6 15 15 14 13 14 15 13 J- 27 38 30 24 18 29 15 V 0 J 0 J 0 J 0 J 0 J 0 0 0 0 0 56 52 49 56 57 58 57 23 24 48 15 36 28 55 58 57 56 50 56 60 53 J- 23 36 13 46 31 64 0 Zn 100 92 110 110 100 176 123 154 178 196 230 220 210 230 230 240 240 380 387 385 384 345 345 348 930 900 870 820 900 950 830 J- 1,191 1,132 1,190 1,134 934 996 1,020 D-4 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 7 7 7 7 7 7 7 7 7 7 8 8 8 8 8 8 8 8 8 8 8 8 8 8 9 9 9 9 9 9 9 9 9 9 Sample ID WS-SO-01-XX WS-SO-04-XX WS-SO-15-XX WS-SO-22-XX WS-SO-34-XX WS-SO-01-XC WS-SO-04-XC WS-SO-15-XC WS-SO-22-XC WS-SO-34-XC WS-SO-02-XX WS-SO-16-XX WS-SO-18-XX WS-SO-21-XX WS-SO-24-XX WS-SO-29-XX WS-SO-37-XX WS-SO-02-XC WS-SO-16-XC WS-SO-18-XC WS-SO-21-XC WS-SO-24-XC WS-SO-29-XC WS-SO-37-XC WS-SO-13-XX WS-SO-19-XX WS-SO-28-XX WS-SO-32-XX WS-SO-36-XX WS-SO-13-XC WS-SO-19-XC WS-SO-28-XC WS-SO-32-XC WS-SO-36-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 41 J- 45 J- 48 J- 41 J- 45 J- 144 152 140 137 136 130 J- 110 J- 130 J- 120 J- 97 J- 120 J- 120 J- 178 170 194 177 202 213 202 200 J- 150 J- 120 J- 190 J- 120 J- 208 178 258 237 260 As 1900 2000 2300 1900 2000 2,917 2,719 2,780 1,689 2,066 4200 3900 4100 3900 3600 3800 4100 5,187 4,682 3,655 4,194 4,123 3,683 4,497 5800 5000 4200 5500 3800 7,772 4,948 5,176 5,696 6,570 Cd 47 50 56 47 50 67 102 44 76 47 98 91 95 90 81 90 95 145 122 120 114 82 98 62 150 130 100 140 92 139 184 130 131 107 Cr 100 94 82 84 91 85 81 64 63 60 49 59 63 43 54 51 63 101 98 51 53 66 54 54 51 67 Cu 590 640 720 620 660 725 658 734 695 597 1,300 1,300 1,300 1,200 1,100 1,200 1,300 1,266 1,259 1,211 1,144 932 1,052 1,071 1800 1500 1200 1700 1100 1,511 1,559 1,207 1,331 1,260 Fe 32,000 34,000 37,000 33,000 36,000 29,297 25,925 29,457 27,447 23,244 44,000 42,000 44,000 40,000 38,000 40,000 42,000 33,774 34,523 31,756 32,103 24,425 27,220 28,622 47,000 39,000 33,000 44,000 30,000 35,738 39,189 27,159 29,668 29,661 Pb 18,000 20,000 24,000 17,000 22,000 42,266 39,796 42,430 37,445 30,445 35,000 24,000 37,000 43,000 27,000 42,000 26,000 64,837 61,339 59,680 56,773 40,706 48,582 48,690 45,000 24,000 30,000 30,000 45,000 47,796 48,951 39,360 41,616 39,863 Hg 5.8 J 6.5 5.8 4.8 5.4 90 65 17 15 17 14 16 15 14 30 46 43 116 100 28 11 12 11 11 13 84 90 52 48 D-5 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 7 7 7 7 7 7 7 7 7 7 8 8 8 8 8 8 8 8 8 8 8 8 8 8 9 9 9 9 9 9 9 9 9 9 Sample ID WS-SO-01-XX WS-SO-04-XX WS-SO-15-XX WS-SO-22-XX WS-SO-34-XX WS-SO-01-XC WS-SO-04-XC WS-SO-15-XC WS-SO-22-XC WS-SO-34-XC WS-SO-02-XX WS-SO-16-XX WS-SO-18-XX WS-SO-21-XX WS-SO-24-XX WS-SO-29-XX WS-SO-37-XX WS-SO-02-XC WS-SO-16-XC WS-SO-18-XC WS-SO-21-XC WS-SO-24-XC WS-SO-29-XC WS-SO-37-XC WS-SO-13-XX WS-SO-19-XX WS-SO-28-XX WS-SO-32-XX WS-SO-36-XX WS-SO-13-XC WS-SO-19-XC WS-SO-28-XC WS-SO-32-XC WS-SO-36-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 66 62 58 57 60 42 38 79 67 65 57 60 62 51 54 55 63 95 85 42 42 90 80 39 75 74 59 73 55 112 43 90 97 100 Se 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1.1 J 1.9 1.6 2.1 1.7 3 126 44 3.7 3.7 2.3 3.7 1.7 14 Ag 69 J- 76 J- 90 J- 72 J- 78 J- 105 99 104 86 59 150 J- 150 J- 140 J- 150 J- 140 J- 140 J- 140 J- 195 182 199 179 105 144 117 170 J- 160 J- 130 J- 190 J- 120 J- 206 223 137 163 144 V 42 44 52 44 47 0 0 0 0 0 36 35 36 33 30 33 34 0 17 41 0 12 0 0 24 20 16 23 15 0 0 0 73 77 Zn 3,000 3,100 3,400 3,000 3,200 4,227 4,061 4,265 4,070 3,534 6,000 5,700 5,900 5,500 5,200 5,500 5,800 7,030 6,880 6,777 6,552 5,451 5,972 5,885 9,000 7,700 6,100 8,500 5,700 9,997 10,289 8,400 8,948 8,632 D-6 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 10 10 10 10 10 10 10 10 10 10 10 10 10 10 11 11 11 11 11 11 11 11 11 11 12 12 12 12 12 12 12 12 12 12 12 12 12 12 Sample ID BN-SO-01-XX BN-SO-10-XX BN-SO-15-XX BN-SO-18-XX BN-SO-28-XX BN-SO-31-XX BN-SO-35-XX BN-SO-01-XC BN-SO-10-XC BN-SO-15-XC BN-SO-18-XC BN-SO-28-XC BN-SO-31-XC BN-SO-35-XC BN-SO-02-XX BN-SO-04-XX BN-SO-17-XX BN-SO-22-XX BN-SO-27-XX BN-SO-02-XC BN-SO-04-XC BN-SO-17-XC BN-SO-22-XC BN-SO-27-XC BN-SO-03-XX BN-SO-06-XX BN-SO-08-XX BN-SO-13-XX BN-SO-20-XX BN-SO-30-XX BN-SO-34-XX BN-SO-03-XC BN-SO-06-XC BN-SO-08-XC BN-SO-13-XC BN-SO-20-XC BN-SO-30-XC BN-SO-34-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 1.3 UJ 1.3 UJ 1.3 UJ 1.3 U 1.5 1.3 1.4 10 4 8 8 0 7 9 11 9.1 9.3 7.3 9.6 12 13 13 4 23 65 60 57 65 57 64 68 61 66 63 70 62 63 62 As 38 50 34 37 35 41 37 47 64 79 74 89 84 89 140 120 110 98 110 164 160 130 203 155 620 600 570 320 540 630 630 684 751 731 715 752 597 652 Cd 0.94 1.2 0.82 0.89 0.87 1 0.98 11 25 33 25 50 42 39 34 39 26 39 46 73 64 290 280 270 150 260 300 290 298 284 319 326 321 307 312 Cr 120 110 110 110 100 140 120 86 64 82 101 92 85 78 90 79 79 65 78 43 56 62 50 36 120 94 100 98 88 100 110 75 104 91 60 76 61 44 Cu 32 35 29 29 28 33 30 26 37 31 30 39 46 45 170 140 140 110 130 149 146 162 158 156 840 810 750 410 730 860 830 850 869 851 848 837 837 873 Fe 24,000 24,000 22,000 22,000 22,000 26,000 23,000 17,877 18,087 18,208 18,517 18,150 18,130 18,569 28,000 24,000 23,000 20,000 24,000 17,560 18,022 18,512 18,691 18,679 25,000 24,000 22,000 17,000 22,000 26,000 25,000 21,467 21,431 21,601 21,842 21,577 21,784 22,434 Pb 63 140 56 59 58 65 60 115 126 93 84 88 163 134 840 700 680 590 660 1,155 1,154 1,176 1,137 1,192 4,700 4,500 4,300 2,400 4,100 4,800 4,700 6,485 6,565 6,593 6,781 6,406 6,448 6,660 Hg 0.13 0.14 0.15 0.13 0.16 0.14 0.15 2 5 0.37 0.36 0.39 0.37 0.38 1.6 2 2 1.6 1.6 1.6 2 11 9 D-7 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 10 10 10 10 10 10 10 10 10 10 10 10 10 10 11 11 11 11 11 11 11 11 11 11 12 12 12 12 12 12 12 12 12 12 12 12 12 12 Sample ID BN-SO-01-XX BN-SO-10-XX BN-SO-15-XX BN-SO-18-XX BN-SO-28-XX BN-SO-31-XX BN-SO-35-XX BN-SO-01-XC BN-SO-10-XC BN-SO-15-XC BN-SO-18-XC BN-SO-28-XC BN-SO-31-XC BN-SO-35-XC BN-SO-02-XX BN-SO-04-XX BN-SO-17-XX BN-SO-22-XX BN-SO-27-XX BN-SO-02-XC BN-SO-04-XC BN-SO-17-XC BN-SO-22-XC BN-SO-27-XC BN-SO-03-XX BN-SO-06-XX BN-SO-08-XX BN-SO-13-XX BN-SO-20-XX BN-SO-30-XX BN-SO-34-XX BN-SO-03-XC BN-SO-06-XC BN-SO-08-XC BN-SO-13-XC BN-SO-20-XC BN-SO-30-XC BN-SO-34-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 63 54 58 59 54 71 63 54 69 60 85 66 71 61 54 48 47 40 46 32 33 57 59 34 100 92 94 71 84 99 100 83 72 79 69 86 76 82 Se 1.3 U 1.2 J 1.3 U 1.3 1.3 U 1.3 U 1.2 J 2 4.3 2.9 2.7 2.8 3.7 6 72 17 15 14 9.2 14 17 17 67 6 114 65 101 Ag 1.3 UJ 1.3 UJ 1.3 UJ 0.94 U 0.77 U 0.97 U 0.85 U 11 11 18 8 6 7.6 6.5 6.3 5.4 6.1 14 14 42 41 38 21 37 44 42 33 44 41 65 31 37 58 V 55 55 49 46 48 54 50 0 15 34 0 0 46 44 60 50 49 43 52 29 0 42 14 24 48 48 39 37 44 50 49 61 44 0 0 0 0 0 Zn 92 110 89 88 81 94 87 155 172 157 169 159 206 193 470 400 390 330 380 665 643 646 669 661 2,300 2,300 2,200 1,200 2,100 2,400 2,300 3,299 3,454 3,331 3,358 3,356 3,325 3,406 D-8 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 13 13 13 13 13 13 13 13 13 13 14 14 14 14 14 14 14 14 14 14 15 15 15 15 15 15 15 15 15 15 16 16 16 16 16 16 16 16 16 16 Sample ID BN-SO-07-XX BN-SO-16-XX BN-SO-21-XX BN-SO-25-XX BN-SO-33-XX BN-SO-07-XC BN-SO-16-XC BN-SO-21-XC BN-SO-25-XC BN-SO-33-XC BN-SO-05-XX BN-SO-19-XX BN-SO-26-XX BN-SO-29-XX BN-SO-32-XX BN-SO-05-XC BN-SO-19-XC BN-SO-26-XC BN-SO-29-XC BN-SO-32-XC CN-SO-01-XX CN-SO-04-XX CN-SO-08-XX CN-SO-10-XX CN-SO-11-XX CN-SO-01-XC CN-SO-04-XC CN-SO-08-XC CN-SO-10-XC CN-SO-11-XC AS-SO-02-XX AS-SO-06-XX AS-SO-10-XX AS-SO-11-XX AS-SO-13-XX AS-SO-02-XC AS-SO-06-XC AS-SO-10-XC AS-SO-11-XC AS-SO-13-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 110 J- 120 J- 150 J- 82 J- 100 J- 100 99 105 103 100 160 J- 150 J- 150 J- 150 J- 160 J- 136 131 134 130 132 13 J- 13 J- 15 J- 13 J- 17 J- 16 19 19 14 21 2.6 UJ 2.4 UJ 1.9 J- 3.7 J- 2.4 UJ 14 12 12 14 13 As 990 J+ 1,100 J+ 1,300 J+ 700 J 1,100 1,133 1,134 1,120 1,016 1,243 1,600 1,600 1,700 1,600 1,600 1,935 1,673 1,719 1,751 1,843 13 11 15 13 16 99 111 40 83 93 18 19 18 22 20 85 85 34 42 41 Cd 520 570 660 370 J- 640 601 561 586 592 599 850 860 900 880 860 808 811 821 834 852 21 21 25 22 30 20 19 20 50 52 48 63 57 64 33 63 62 47 Cr 82 86 110 64 J- 100 74 57 105 39 86 79 82 86 84 87 63 45 45 190 200 210 200 240 158 179 179 170 155 180 190 180 230 200 146 225 172 154 175 Cu 1,400 1,500 1,700 930 J- 1,600 1,456 1,457 1,466 1,369 1,527 2,200 2,200 2,400 2,300 2,300 2,193 2,199 2,194 2,254 2,187 700 680 740 760 860 731 741 737 752 729 140 130 110 150 150 311 319 330 349 350 Fe 23,000 25,000 30,000 16,000 J- 27,000 23,645 23,360 24,645 22,952 25,053 26,000 26,000 27,000 26,000 26,000 26,751 27,009 26,274 27,470 26,292 38,000 37,000 43,000 39,000 47,000 34,316 34,495 32,236 33,088 33,039 48,000 52,000 45,000 52,000 52,000 33,843 36,284 36,503 38,108 36,984 Pb 6,900 8,100 8,900 5,400 J- 8,000 8,902 8,699 8,942 8,762 8,705 12,000 12,000 12,000 12,000 12,000 10,794 10,790 10,750 10,894 10,562 1,200 1,200 1,300 1,200 1,600 1,738 1,901 1,790 1,755 1,806 1,600 1,600 1,400 2,100 1,700 2,497 2,390 2,495 2,669 2,579 Hg 3.4 3.4 3.6 3.8 4 5 5 5.4 5.4 5.4 0.13 0.14 0.16 0.12 0.15 0.76 0.74 0.78 0.72 0.79 10 15 17 12 8 D-9 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 13 13 13 13 13 13 13 13 13 13 14 14 14 14 14 14 14 14 14 14 15 15 15 15 15 15 15 15 15 15 16 16 16 16 16 16 16 16 16 16 Sample ID BN-SO-07-XX BN-SO-16-XX BN-SO-21-XX BN-SO-25-XX BN-SO-33-XX BN-SO-07-XC BN-SO-16-XC BN-SO-21-XC BN-SO-25-XC BN-SO-33-XC BN-SO-05-XX BN-SO-19-XX BN-SO-26-XX BN-SO-29-XX BN-SO-32-XX BN-SO-05-XC BN-SO-19-XC BN-SO-26-XC BN-SO-29-XC BN-SO-32-XC CN-SO-01-XX CN-SO-04-XX CN-SO-08-XX CN-SO-10-XX CN-SO-11-XX CN-SO-01-XC CN-SO-04-XC CN-SO-08-XC CN-SO-10-XC CN-SO-11-XC AS-SO-02-XX AS-SO-06-XX AS-SO-10-XX AS-SO-11-XX AS-SO-13-XX AS-SO-02-XC AS-SO-06-XC AS-SO-10-XC AS-SO-11-XC AS-SO-13-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni Se Ag V Zn 120 26 70 41 4,000 130 29 77 44 4,400 160 35 88 52 5,100 88 J- 19 J- 48 J- 28 J- 2,900 J- 150 34 81 48 5,100 100 47 75 31 5,643 71 15 73 41 5,547 103 20 76 0 5,498 99 66 0 5,524 117 84 0 5,746 160 48 110 39 6,700 160 48 120 39 6,700 160 49 120 40 7,000 160 48 120 41 6,800 160 48 120 39 6,700 113 100 123 0 7,367 134 72 106 0 7,318 107 117 0 7,323 126 128 0 7,482 125 115 30 7,359 240 2.2 12 21 3,100 240 1.5 12 22 2,900 280 1.3 U 15 26 3,200 240 1.9 14 22 3,000 320 1.3 U 16 27 3,500 198 18 48 3,910 183 23 0 3,742 184 55 3 51 3,732 185 15 56 3,451 217 3 0 3,451 91 2.6 U 4.5 42 3,300 93 2.6 U 4.8 44 3,500 84 1.1 U 4.4 42 3,000 120 1.1 U 5.6 54 3,800 100 3 5.2 50 3,800 92 5 60 3,543 86 0 3,424 95 00 3,321 86 10 0 3,440 86 80 3,539 D-10 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 17 17 17 17 17 17 17 17 17 17 18 18 18 18 18 18 18 18 18 18 18 18 18 18 19 19 19 19 19 19 19 19 19 19 Sample ID AS-SO-01-XX AS-SO-04-XX AS-SO-07-XX AS-SO-09-XX AS-SO-12-XX AS-SO-01-XC AS-SO-04-XC AS-SO-07-XC AS-SO-09-XC AS-SO-12-XC SB-SO-03-XX SB-SO-06-XX SB-SO-14-XX SB-SO-38-XX SB-SO-41-XX SB-SO-47-XX SB-SO-51-XX SB-SO-03-XC SB-SO-06-XC SB-SO-14-XC SB-SO-38-XC SB-SO-41-XC SB-SO-47-XC SB-SO-51-XC SB-SO-05-XX SB-SO-18-XX SB-SO-30-XX SB-SO-40-XX SB-SO-53-XX SB-SO-05-XC SB-SO-18-XC SB-SO-30-XC SB-SO-40-XC SB-SO-53-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 3.8 J- 6.4 UJ 3.6 J- 2.6 UJ 2.6 UJ 4 6 6 1.2 UJ 1.7 J- 4.1 J- 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 6 0 3 4 9 15 4 1.6 J- 1.2 UJ 3.2 J- 2.2 J- 1.2 UJ 9 0 0 0 13 As 26 22 21 25 J- 29 74 46 45 46 85 9 8 9 10 9 8 9 50 63 82 72 63 77 60 9 10 7 9 10 70 82 65 72 46 Cd 100 110 97 100 J- 120 67 75 105 78 84 0.51 U 0.51 U 0.51 U 0.51 U 0.51 U 0.51 U 0.51 U 10 48 0.51 U 0.51 U 0.51 U 0.51 U 0.51 U 29 34 31 Cr 420 480 380 390 J- 440 371 364 415 523 313 150 140 150 150 160 140 160 104 115 130 148 160 183 119 140 150 94 120 140 132 68 62 153 106 Cu 250 260 240 250 J- 270 591 667 623 629 686 48 44 46 57 58 44 50 28 20 37 27 28 29 33 46 46 27 40 44 5 23 39 37 31 Fe 100,000 110,000 88,000 94,000 J- 93,000 74,049 79,399 78,896 83,038 82,623 38,000 35,000 37,000 37,000 40,000 34,000 40,000 27,814 27,713 27,854 27,016 26,866 27,284 27,183 35,000 38,000 22,000 33,000 37,000 25,964 23,181 25,684 25,849 26,290 Pb 3,200 3,300 2,900 3,200 J- 3,300 6,123 6,244 6,402 6,597 6,547 18 16 17 18 19 16 18 85 88 52 75 87 0 106 16 17 10 15 17 0 68 64 0 41 Hg 1.4 1.3 1.4 1.4 1.4 53 56 51 47 44 62 55 55 56 54 58 54 11 15 16 19 22 9 29 540 280 290 280 270 219 155 187 205 195 D-ll ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 17 17 17 17 17 17 17 17 17 17 18 18 18 18 18 18 18 18 18 18 18 18 18 18 19 19 19 19 19 19 19 19 19 19 Sample ID AS-SO-01-XX AS-SO-04-XX AS-SO-07-XX AS-SO-09-XX AS-SO-12-XX AS-SO-01-XC AS-SO-04-XC AS-SO-07-XC AS-SO-09-XC AS-SO-12-XC SB-SO-03-XX SB-SO-06-XX SB-SO-14-XX SB-SO-38-XX SB-SO-41-XX SB-SO-47-XX SB-SO-51-XX SB-SO-03-XC SB-SO-06-XC SB-SO-14-XC SB-SO-38-XC SB-SO-41-XC SB-SO-47-XC SB-SO-51-XC SB-SO-05-XX SB-SO-18-XX SB-SO-30-XX SB-SO-40-XX SB-SO-53-XX SB-SO-05-XC SB-SO-18-XC SB-SO-30-XC SB-SO-40-XC SB-SO-53-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 180 200 160 170 J- 190 130 153 159 119 133 210 200 210 210 230 200 230 179 197 173 196 171 168 167 200 210 120 180 200 165 139 144 154 158 Se 2.6 U 6.2 U 2.7 2.6 U 2.6 U 24 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 54 1.3 U 1.3 U 1.3 J+ 1.3 U 1.3 U 13 Ag 9.3 12 8.9 9.6 J- 3.2 3 4 9 9 7 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 4 6 6 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 8 16 8 V 66 72 63 65 J- 73 88 0 0 0 37 67 63 66 68 71 62 74 90 36 77 35 0 0 55 61 70 43 58 64 62 0 147 42 74 Zn 6,900 7,400 6,300 6,800 J- 7,500 2,484 2,195 2,196 1,858 2,034 90 82 95 91 96 82 93 109 98 108 114 98 114 102 80 84 50 74 81 92 89 90 106 88 D-12 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 20 20 20 20 20 20 20 20 20 20 21 21 21 21 21 21 21 21 21 21 22 22 22 22 22 22 22 22 22 22 23 23 23 23 23 23 23 23 23 23 Sample ID SB-SO-08-XX SB-SO-11-XX SB-SO-21-XX SB-SO-39-XX SB-SO-42-XX SB-SO-08-XC SB-SO-11-XC SB-SO-21-XC SB-SO-39-XC SB-SO-42-XC SB-SO-22-XX SB-SO-25-XX SB-SO-27-XX SB-SO-35-XX SB-SO-44-XX SB-SO-22-XC SB-SO-25-XC SB-SO-27-XC SB-SO-35-XC SB-SO-44-XC SB-SO-23-XX SB-SO-28-XX SB-SO-32-XX SB-SO-43-XX SB-SO-48-XX SB-SO-23-XC SB-SO-28-XC SB-SO-32-XC SB-SO-43-XC SB-SO-48-XC SB-SO-02-XX SB-SO-07-XX SB-SO-10-XX SB-SO-26-XX SB-SO-50-XX SB-SO-02-XC SB-SO-07-XC SB-SO-10-XC SB-SO-26-XC SB-SO-50-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 5.4 J- 5.7 J- 4.9 J 4.7 J- 4.6 J- 10 11 0 8 13 10 J 6.8 J+ 6.7 J+ 6 J+ 6.8 J+ 10 14 15 14 20 48 J- 42 J- 46 J- 40 J- 39 J- 35 39 38 34 39 44 J- 45 J 62 J 61 J 57 J 49 58 53 53 50 As 13 13 13 13 13 63 71 72 90 120 18 18 18 17 18 124 109 112 119 116 37 36 40 35 36 317 347 349 425 367 23 J- 22 26 30 27 99 72 52 46 74 Cd 0.51 U 0.51 U 0.51 U 0.51 U 0.51 U 26 0.51 U 0.51 U 0.51 U 0.51 U 0.51 U 0 0.1 U 0.1 U 0.1 U 0.1 U 0.1 U 0 12 0 40 0 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 35 38 24 Cr 120 140 130 140 140 109 97 51 133 132 120 120 120 110 120 51 20 53 61 21 21 23 20 21 36 25 130 120 140 160 140 115 118 122 101 134 Cu 39 46 43 46 45 25 26 18 27 5 37 37 37 35 37 16 3 20 22 25 7 7 7.6 6.7 6.9 1 0 0 1 0 43 38 44 50 46 30 26 38 40 39 Fe 32,000 36,000 34,000 34,000 35,000 24,137 24,094 22,026 23,521 24,055 29,000 29,000 29,000 28,000 29,000 18,480 19,155 19,141 19,400 19,543 4,500 4,400 4,900 4,200 4,500 2,818 2,961 2,881 2,850 2,881 35,000 35,000 41,000 46,000 42,000 28,994 29,271 29,497 27,573 28,740 Pb 17 20 18 19 18 0 0 0 0 0 22 22 22 21 22 0 0 0 0 0 36 36 40 34 36 0 0 0 0 0 22 J- 23 27 31 28 49 67 74 83 0 Hg 730 810 740 790 740 656 650 485 632 617 3300 3000 3100 3100 3000 1,057 1,107 1,128 1,233 1,283 8500 8800 8900 7600 8200 1,347 1,494 1,505 1,494 1,496 130 J+ 270 220 260 200 74 87 69 62 74 D-13 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 20 20 20 20 20 20 20 20 20 20 21 21 21 21 21 21 21 21 21 21 22 22 22 22 22 22 22 22 22 22 23 23 23 23 23 23 23 23 23 23 Sample ID SB-SO-08-XX SB-SO-11-XX SB-SO-21-XX SB-SO-39-XX SB-SO-42-XX SB-SO-08-XC SB-SO-11-XC SB-SO-21-XC SB-SO-39-XC SB-SO-42-XC SB-SO-22-XX SB-SO-25-XX SB-SO-27-XX SB-SO-35-XX SB-SO-44-XX SB-SO-22-XC SB-SO-25-XC SB-SO-27-XC SB-SO-35-XC SB-SO-44-XC SB-SO-23-XX SB-SO-28-XX SB-SO-32-XX SB-SO-43-XX SB-SO-48-XX SB-SO-23-XC SB-SO-28-XC SB-SO-32-XC SB-SO-43-XC SB-SO-48-XC SB-SO-02-XX SB-SO-07-XX SB-SO-10-XX SB-SO-26-XX SB-SO-50-XX SB-SO-02-XC SB-SO-07-XC SB-SO-10-XC SB-SO-26-XC SB-SO-50-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 180 200 190 200 200 154 134 120 135 135 160 160 170 160 170 114 119 117 121 113 26 26 28 24 25 6 6 6 24 6 180 170 200 220 200 162 160 166 173 190 Se 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 52 25 0.22 J 0.26 U 0.36 0.26 U 0.26 U 1.2 U 1.4 2.8 3.4 2.9 12 Ag 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 1 18 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 12 29 0.26 UJ 0.26 UJ 0.1 UJ 0.26 UJ 0.1 UJ 7 5 15 5 1.2 UJ 1.6 1.8 1.8 1.8 12 18 18 15 V 57 66 58 62 65 29 96 28 53 63 52 54 54 50 53 22 121 69 96 68 13 13 14 13 13 147 93 156 162 135 59 53 59 68 61 0 0 0 43 38 Zn 70 84 75 77 78 74 72 60 77 98 64 J- 63 65 62 64 58 67 57 60 67 8 8 9 8 8 18 0 0 13 0 88 86 100 110 100 113 114 117 103 114 D-14 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 24 24 24 24 24 24 24 24 24 24 25 25 25 25 25 25 25 25 25 25 26 26 26 26 26 26 26 26 26 26 27 27 27 27 27 27 27 27 27 27 Sample ID SB-SO-01-XX SB-SO-16-XX SB-SO-24-XX SB-SO-45-XX SB-SO-52-XX SB-SO-01-XC SB-SO-16-XC SB-SO-24-XC SB-SO-45-XC SB-SO-52-XC SB-SO-13-XX SB-SO-19-XX SB-SO-33-XX SB-SO-37-XX SB-SO-55-XX SB-SO-13-XC SB-SO-19-XC SB-SO-33-XC SB-SO-37-XC SB-SO-55-XC SB-SO-12-XX SB-SO-15-XX SB-SO-17-XX SB-SO-46-XX SB-SO-54-XX SB-SO-12-XC SB-SO-15-XC SB-SO-17-XC SB-SO-46-XC SB-SO-54-XC KP-SE-08-XX KP-SE-11-XX KP-SE-17-XX KP-SE-25-XX KP-SE-30-XX KP-SE-08-XC KP-SE-11-XC KP-SE-17-XC KP-SE-25-XC KP-SE-30-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 180 J 170 J 180 J 180 J 150 J 123 129 105 122 131 430 J 310 J 350 J 340 J 340 J 280 210 259 258 278 620 J 600 J- 800 J+ 740 J+ 280 428 419 257 417 425 6.2 5.6 4.9 6 5.7 13 16 17 12 14 As 65 64 66 63 62 83 108 103 88 94 160 100 110 130 120 194 174 195 172 195 190 170 J- 210 190 31 266 298 215 259 260 3 3 3 3 3 126 82 76 0 40 Cd 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 33 25 1 U 0.5 U 0.5 U 1 U 0.5 U 28 24 30 1 U 1 U 1 U 1 U 0.2 U 27 29 28 0.11 U 0.11 U 0.11 U 0.11 U 0.11 U 32 28 Cr 140 140 150 140 140 132 115 76 161 110 140 100 100 120 120 92 92 170 99 100 91 J- 110 120 25 132 133 32 133 204 88 96 98 99 83 96 94 92 113 93 Cu 46 45 49 45 47 44 30 25 37 38 46 32 33 39 37 32 22 19 35 35 33 30 J- 37 35 5.8 20 28 22 24 28 3.8 4.1 4.1 4.3 3.6 0 1 1 1 1 Fe 47,000 47,000 49,000 47,000 46,000 32,072 30,888 28,359 30,355 29,892 61,000 42,000 45,000 51,000 49,000 35,473 31,909 34,068 36,020 36,018 55,000 51,000 J- 61,000 57,000 8,600 39,828 39,562 33,967 39,119 39,886 840 940 940 960 830 966 940 1,036 1,039 1,048 Pb 30 30 32 30 29 67 0 0 83 76 36 25 28 31 29 58 0 0 76 105 43 40 J- 48 47 5 J- 91 0 0 80 84 300 J- 310 J- 300 J- 310 J- 300 J- 442 450 458 512 491 Hg 400 480 420 450 430 158 141 111 168 153 850 740 870 790 900 339 220 293 310 338 1,400 1,100 1,200 670 560 570 524 337 504 495 0.089 U 0.079 U 0.082 U 0.096 U 0.1 U 3 3 D-15 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 24 24 24 24 24 24 24 24 24 24 25 25 25 25 25 25 25 25 25 25 26 26 26 26 26 26 26 26 26 26 27 27 27 27 27 27 27 27 27 27 Sample ID SB-SO-01-XX SB-SO-16-XX SB-SO-24-XX SB-SO-45-XX SB-SO-52-XX SB-SO-01-XC SB-SO-16-XC SB-SO-24-XC SB-SO-45-XC SB-SO-52-XC SB-SO-13-XX SB-SO-19-XX SB-SO-33-XX SB-SO-37-XX SB-SO-55-XX SB-SO-13-XC SB-SO-19-XC SB-SO-33-XC SB-SO-37-XC SB-SO-55-XC SB-SO-12-XX SB-SO-15-XX SB-SO-17-XX SB-SO-46-XX SB-SO-54-XX SB-SO-12-XC SB-SO-15-XC SB-SO-17-XC SB-SO-46-XC SB-SO-54-XC KP-SE-08-XX KP-SE-11-XX KP-SE-17-XX KP-SE-25-XX KP-SE-30-XX KP-SE-08-XC KP-SE-11-XC KP-SE-17-XC KP-SE-25-XC KP-SE-30-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 190 190 200 190 190 170 139 130 149 151 180 120 130 150 140 125 121 100 132 128 110 100 J- 120 120 20 122 109 56 111 110 42 46 47 47 39 39 36 42 46 47 Se 1.8 1.9 2.5 2.8 1.8 4.4 2.5 3 2.5 U 2.5 2.5 U 3.4 2.8 2.6 0.5 U 0.27 U 0.43 0.27 U 0.26 U 0.24 U 2 41 41 Ag 2.3 2.2 2.3 2.1 J- 2.2 16 6 22 4 20 2.2 UJ 1.8 2 J 2 UJ 2.2 J 24 27 13 29 37 2.1 UJ 1.6 UJ 2.3 UJ 2.2 UJ 0.5 UJ 23 13 0.27 UJ 0.27 UJ 0.27 UJ 0.27 UJ 0.27 UJ 12 5 2 V 65 65 67 63 64 57 24 0 59 28 74 51 52 63 61 64 0 148 179 48 59 52 J- 60 57 11 0 40 0 33 9 4 4 4 4 4 26 0 0 0 32 Zn 95 97 95 93 90 96 84 67 91 96 70 51 56 58 60 56 57 57 68 57 42 36 J- 42 41 6 41 32 35 34 37 5 6 5 5 5 0 35 25 25 18 D-16 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 28 28 28 28 28 28 28 28 28 28 29 29 29 29 29 29 29 29 29 29 29 29 29 29 30 30 30 30 30 30 30 30 30 30 Sample ID KP-SE-01-XX KP-SE-12-XX KP-SE-14-XX KP-SE-19-XX KP-SE-28-XX KP-SE-01-XC KP-SE-12-XC KP-SE-14-XC KP-SE-19-XC KP-SE-28-XC TL-SE-04-XX TL-SE-10-XX TL-SE-12-XX TL-SE-15-XX TL-SE-20-XX TL-SE-24-XX TL-SE-26-XX TL-SE-04-XC TL-SE-10-XC TL-SE-12-XC TL-SE-15-XC TL-SE-20-XC TL-SE-24-XC TL-SE-26-XC TL-SE-03-XX TL-SE-19-XX TL-SE-23-XX TL-SE-25-XX TL-SE-31-XX TL-SE-03-XC TL-SE-19-XC TL-SE-23-XC TL-SE-25-XC TL-SE-31-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 3.2 3.1 11 J- 3 3.3 4 5 13 5 1.2 U 1.2 U 1.2 U 1.2 U 1.2 U 1.2 U 1.2 U 0 5 7 5 10 9 16 2.5 U 2.5 U 2.5 U 2.5 U 2.5 U 11 6 10 11 9 As 2 2 2 2 2 70 27 107 81 36 10 10 10 9 10 11 10 58 0 53 30 45 78 42 9 10 9 10 10 67 32 74 27 79 Cd 0.1 U 0.1 U 0.1 U 0.1 U 0.1 U 11 26 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 12 1 U 1 U 1 U 1 U 1 U 12 16 Cr 34 42 46 J- 44 45 72 59 61 45 70 62 64 66 54 64 67 62 7 36 26 91 96 92 91 110 Cu 2.2 2.5 2.7 J+ 2.3 2.3 8 1 1 1 1 1,900 2,000 2,100 1,800 2,000 2,100 2,000 2,586 2,606 2,626 2,461 2,718 2,911 2,631 1,600 1,700 1,600 1,600 1,800 1,879 2,405 2,272 2,281 2,096 Fe 480 510 520 J- 510 520 651 509 635 640 646 42,000 43,000 44,000 36,000 42,000 43,000 40,000 36,085 36,600 36,634 35,872 37,221 37,288 36,523 63,000 66,000 64,000 62,000 74,000 52,922 56,855 57,909 58,350 55,112 Pb 310 J- 320 J- 680 J- 330 320 405 343 423 452 453 32 35 34 28 32 37 34 98 144 133 122 119 135 195 12 13 12 11 13 139 60 106 115 160 Hg 0.053 U 0.06 U 0.065 U 0.044 U 0.056 U 3 2 2 0.26 J- 0.19 J- 0.22 J- 0.28 J- 0.26 J- 0.26 J- 0.24 J- 6 0.32 J- 0.32 J- 0.41 J- 0.44 J- 0.57 J- D-17 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 28 28 28 28 28 28 28 28 28 28 29 29 29 29 29 29 29 29 29 29 29 29 29 29 30 30 30 30 30 30 30 30 30 30 Sample ID KP-SE-01-XX KP-SE-12-XX KP-SE-14-XX KP-SE-19-XX KP-SE-28-XX KP-SE-01-XC KP-SE-12-XC KP-SE-14-XC KP-SE-19-XC KP-SE-28-XC TL-SE-04-XX TL-SE-10-XX TL-SE-12-XX TL-SE-15-XX TL-SE-20-XX TL-SE-24-XX TL-SE-26-XX TL-SE-04-XC TL-SE-10-XC TL-SE-12-XC TL-SE-15-XC TL-SE-20-XC TL-SE-24-XC TL-SE-26-XC TL-SE-03-XX TL-SE-19-XX TL-SE-23-XX TL-SE-25-XX TL-SE-31-XX TL-SE-03-XC TL-SE-19-XC TL-SE-23-XC TL-SE-25-XC TL-SE-31-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 16 20 23 J- 22 22 27 20 24 23 18 71 72 75 63 74 77 70 116 115 117 123 89 107 100 110 120 110 110 130 154 137 121 115 115 Se 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 11 47 27 1.2 U 1.2 U 1.2 U 1.2 U 1.2 U 1.2 U 1.2 U 5 2.5 U 2.5 U 2.5 U 2.5 U 2.5 U 3 Ag 0.26 UJ 0.26 UJ 0.26 UJ 0.26 U 0.26 U 3 3 1.3 1.2 U 1.2 U 1 U 1.2 U 1.3 U 1.2 U 13 15 25 17 0.94 U 1.1 U 1.3 U 0.94 U 1.2 U 6 41 23 54 15 V 2 J 2 J 3 J 2 J 2 J 0 0 0 21 0 95 95 100 84 100 100 96 0 0 0 0 0 0 54 140 150 150 150 170 0 0 0 0 66 Zn 6 8 7 7 6 33 25 30 38 35 160 160 170 140 160 170 160 183 180 165 179 174 168 192 200 210 200 200 230 113 98 95 93 97 D-18 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 31 31 31 31 31 31 31 31 31 31 31 31 31 31 32 32 32 32 32 32 32 32 32 32 32 32 32 32 33 33 33 33 33 33 33 33 33 33 Sample ID TL-SE-01-XX TL-SE-11-XX TL-SE-14-XX TL-SE-18-XX TL-SE-22-XX TL-SE-27-XX TL-SE-29-XX TL-SE-01-XC TL-SE-11-XC TL-SE-14-XC TL-SE-18-XC TL-SE-22-XC TL-SE-27-XC TL-SE-29-XC LV-SE-02-XX LV-SE-10-XX LV-SE-22-XX LV-SE-25-XX LV-SE-31-XX LV-SE-35-XX LV-SE-50-XX LV-SE-02-XC LV-SE-10-XC LV-SE-22-XC LV-SE-25-XC LV-SE-31-XC LV-SE-35-XC LV-SE-50-XC LV-SE-12-XX LV-SE-26-XX LV-SE-33-XX LV-SE-39-XX LV-SE-42-XX LV-SE-12-XC LV-SE-26-XC LV-SE-33-XC LV-SE-39-XC LV-SE-42-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 1.2 UJ 1.2 UJ 1.2 UJ 1.2 UJ 1.2 UJ 1.2 UJ 1.2 UJ 0 7 3 4 9 12 10 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 2.5 U 5 9 10 5 0 0 0 2.6 U 2.6 U 2.6 U 2.6 U 2.7 U 8 7 10 11 As 9 15 10 10 11 10 11 68 86 58 51 37 16 45 28 34 30 31 32 31 J- 29 74 82 81 85 87 73 79 190 220 170 190 170 230 243 227 291 261 Cd 0.5 U 0.5 U 0.27 J 0.5 U 0.5 U 0.28 J 0.22 J 19 13 1 0.51 U 0.51 U 0.51 U 0.51 U 0.51 U 0.51 U 1 U 33 35 11 11 25 1 U 1 U 1 U 1 U 1.1 U Cr 110 140 110 150 150 130 140 124 102 87 98 149 141 93 72 84 69 74 78 74 J- 74 39 46 44 49 55 64 52 58 50 98 133 81 Cu 1,400 1,600 1,500 1,300 1,700 1,500 1,600 1,462 1,883 1,900 1,876 1,865 1,932 1,809 33 42 33 36 36 35 34 6 30 25 23 21 20 5 34 39 31 35 30 32 32 35 43 26 Fe 19,000 28,000 18,000 24,000 26,000 19,000 23,000 26,263 34,010 33,304 32,929 33,004 32,418 31,056 23,000 28,000 23,000 25,000 25,000 24,000 J- 24,000 19,902 20,112 19,644 20,308 19,882 20,470 19,573 72,000 83,000 66,000 74,000 65,000 51,313 53,305 53,895 54,680 54,288 Pb 48 J- 54 J- 50 J- 46 J- 54 J- 51 J- 51 J- 154 145 141 193 181 187 119 20 J- 25 J- 22 J- 23 J- 49 J- 22 J- 24 J- 80 0 59 125 57 96 69 19 J- 25 J- 21 J- 22 J- 22 J- 155 120 183 0 104 Hg 0.074 U 0.021 U 0.08 U 0.025 U 0.082 U 0.02 U 0.076 U 5 5 3 4 18 1 0.02 U 0.023 U 1.1 1 1 1.4 1.2 13 7 6 19 5.6 6 6.8 8 4.3 D-19 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 31 31 31 31 31 31 31 31 31 31 31 31 31 31 32 32 32 32 32 32 32 32 32 32 32 32 32 32 33 33 33 33 33 33 33 33 33 33 Sample ID TL-SE-01-XX TL-SE-11-XX TL-SE-14-XX TL-SE-18-XX TL-SE-22-XX TL-SE-27-XX TL-SE-29-XX TL-SE-01-XC TL-SE-11-XC TL-SE-14-XC TL-SE-18-XC TL-SE-22-XC TL-SE-27-XC TL-SE-29-XC LV-SE-02-XX LV-SE-10-XX LV-SE-22-XX LV-SE-25-XX LV-SE-31-XX LV-SE-35-XX LV-SE-50-XX LV-SE-02-XC LV-SE-10-XC LV-SE-22-XC LV-SE-25-XC LV-SE-31-XC LV-SE-35-XC LV-SE-50-XC LV-SE-12-XX LV-SE-26-XX LV-SE-33-XX LV-SE-39-XX LV-SE-42-XX LV-SE-12-XC LV-SE-26-XC LV-SE-33-XC LV-SE-39-XC LV-SE-42-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 180 210 180 190 210 200 200 156 220 198 199 206 232 209 160 200 170 170 180 170 J- 170 115 119 106 141 111 116 113 71 83 66 74 67 71 72 72 102 99 Se 1.2 U 1.2 U 1.2 U 1.2 U 1.2 U 1.2 U 1.2 U 64 37 3.8 4.7 5.2 5.1 5.1 5 3.3 3 6.1 2.8 5.1 3.4 22 Ag 5.7 J- 5.5 J- 5.7 J- 6.3 J- 6.5 J- 7.8 J- 5.9 J- 33 21 24 26 23 26 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 2.5 U 11 6 7 10 8 2 21 2.6 U 2.6 U 2.6 U 2.6 U 2.7 U 3 4 5 2 V 75 85 73 70 80 67 80 0 0 64 54 0 65 44 53 66 51 56 58 55 J- 57 55 73 23 0 0 45 82 72 86 67 74 64 25 27 0 0 0 Zn 130 140 140 120 150 140 140 97 104 107 93 107 109 104 65 77 66 70 70 67 J- 65 115 97 127 124 113 91 100 66 75 59 66 57 48 37 40 31 41 D-20 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 34 34 34 34 34 34 34 34 34 34 35 35 35 35 35 35 35 35 35 35 36 36 36 36 36 36 36 36 36 36 37 37 37 37 37 37 37 37 37 37 Sample ID LV-SE-09-XX LV-SE-19-XX LV-SE-27-XX LV-SE-36-XX LV-SE-38-XX LV-SE-09-XC LV-SE-19-XC LV-SE-27-XC LV-SE-36-XC LV-SE-38-XC LV-SE-07-XX LV-SE-18-XX LV-SE-23-XX LV-SE-45-XX LV-SE-48-XX LV-SE-07-XC LV-SE-18-XC LV-SE-23-XC LV-SE-45-XC LV-SE-48-XC LV-SE-01-XX LV-SE-14-XX LV-SE-21-XX LV-SE-24-XX LV-SE-32-XX LV-SE-01-XC LV-SE-14-XC LV-SE-21-XC LV-SE-24-XC LV-SE-32-XC LV-SE-08-XX LV-SE-16-XX LV-SE-28-XX LV-SE-30-XX LV-SE-47-XX LV-SE-08-XC LV-SE-16-XC LV-SE-28-XC LV-SE-30-XC LV-SE-47-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 6.7 U 6.7 U 6.7 U 6.7 U 6.7 U 0 11 10 15 0 6.7 UJ 6.7 UJ 6.6 UJ 6.7 UJ 6.6 UJ 12 11 22 35 28 1.5 UJ 1.5 UJ 1.5 UJ 1.5 UJ 1.4 UJ 118 80 98 98 107 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 0 1 1 6 0 As 450 500 530 550 480 513 517 488 545 503 780 800 660 650 680 692 670 705 642 585 6 5 7 5 6 91 70 72 66 73 30 29 31 30 31 69 83 71 57 93 Cd 2.7 U 2.7 U 2.7 U 2.7 U 2.7 U 24 18 0 2.7 U 2.7 U 2.6 U 2.7 U 2.6 U 12 9 0.76 0.74 0.84 0.68 0.87 28 0.52 U 0.52 U 0.52 U 0.52 U 0.52 U 36 52 34 Cr 48 55 56 60 52 270 384 86 92 57 61 53 50 52 314 702 346 4 4 4 4 4 54 53 59 58 56 40 58 Cu 34 37 39 40 36 40 2 3 36 4 48 49 40 40 42 47 2 28 54 1 18 16 19 15 16 1 14 0 0 1 23 22 25 25 23 6 5 5 5 23 Fe 150,000 160,000 180,000 180,000 160,000 105,797 104,569 103,211 107,069 105,744 200,000 210,000 170,000 170,000 180,000 132,559 133,997 129,948 120,254 124,294 1,100 980 970 840 860 416 446 455 437 433 23,000 22,000 25,000 24,000 23,000 20,743 20,064 20,981 20,597 19,257 Pb 14 J- 17 J- 16 J- 21 J- 15 J- 0 166 257 0 0 11 11 8 8 9 270 356 192 0 445 17 14 18 14 14 43 22 22 27 32 55 53 59 58 57 137 177 165 193 145 Hg 6 7.2 11 8.5 7.9 5.5 5.4 5 5.6 7.3 109 0.098 U 0.056 U 0.048 U 0.053 U 0.052 U 3 2 5.2 5.4 5.4 6.3 4.9 8 12 7 D-21 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 34 34 34 34 34 34 34 34 34 34 35 35 35 35 35 35 35 35 35 35 36 36 36 36 36 36 36 36 36 36 37 37 37 37 37 37 37 37 37 37 Sample ID LV-SE-09-XX LV-SE-19-XX LV-SE-27-XX LV-SE-36-XX LV-SE-38-XX LV-SE-09-XC LV-SE-19-XC LV-SE-27-XC LV-SE-36-XC LV-SE-38-XC LV-SE-07-XX LV-SE-18-XX LV-SE-23-XX LV-SE-45-XX LV-SE-48-XX LV-SE-07-XC LV-SE-18-XC LV-SE-23-XC LV-SE-45-XC LV-SE-48-XC LV-SE-01-XX LV-SE-14-XX LV-SE-21-XX LV-SE-24-XX LV-SE-32-XX LV-SE-01-XC LV-SE-14-XC LV-SE-21-XC LV-SE-24-XC LV-SE-32-XC LV-SE-08-XX LV-SE-16-XX LV-SE-28-XX LV-SE-30-XX LV-SE-47-XX LV-SE-08-XC LV-SE-16-XC LV-SE-28-XC LV-SE-30-XC LV-SE-47-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 55 65 64 70 75 74 74 75 73 74 58 60 50 J 50 J 50 J 55 54 57 65 111 49 46 49 44 47 21 25 17 31 15 110 110 120 120 120 122 84 102 108 96 Se 6.7 U 5.9 J 6.7 U 11 6.7 U 111 10 10 12 9.6 8.2 7.6 5 9 1.5 U 1.5 U 1.5 U 1.5 U 1.4 U 4.8 5 5.8 5.6 4.2 6 Ag 6.7 U 6.7 U 6.7 U 6.7 U 6.7 U 13 14 10 6.7 U 6.7 U 6.6 U 6.7 U 6.6 U 1.5 U 1.5 U 1.5 U 1.5 U 1.4 U 9 4 19 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 4 0 9 15 2 V 100 110 120 120 100 0 0 0 0 0 130 140 120 120 120 0 0 0 15 0 2 J 1 J 2 J 1 J 1 J 0 0 0 0 0 44 42 48 48 45 46 32 16 36 32 Zn 51 J 55 J 58 J 60 J 54 J 24 J 52 J 18 J 19 J 30 J 0 14 J 12 J 14 J 12 J 19 22 53 0 0 29 61 59 65 66 65 116 103 100 92 107 D-22 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 38 38 38 38 38 38 38 38 38 38 39 39 39 39 39 39 39 39 39 39 39 39 39 39 40 40 40 40 40 40 40 40 40 40 Sample ID LV-SE-ll-XX LV-SE-29-XX LV-SE-44-XX LV-SE-46-XX LV-SE-52-XX LV-SE-11-XC LV-SE-29-XC LV-SE-44-XC LV-SE-46-XC LV-SE-52-XC RF-SE-07-XX RF-SE-12-XX RF-SE-23-XX RF-SE-36-XX RF-SE-42-XX RF-SE-45-XX RF-SE-53-XX RF-SE-07-XC RF-SE-12-XC RF-SE-23-XC RF-SE-36-XC RF-SE-42-XC RF-SE-45-XC RF-SE-53-XC RF-SE-03-XX RF-SE-28-XX RF-SE-38-XX RF-SE-49-XX RF-SE-55-XX RF-SE-03-XC RF-SE-28-XC RF-SE-38-XC RF-SE-49-XC RF-SE-55-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 1.4 UJ 1.4 UJ 1.4 U 0.88 U 1.4 U 17 13 9 11 1.3 U 1.2 U 0.25 U 1.2 U 1.3 UJ 1.3 UJ 1.3 UJ 0 0 0 0 4 9 0 1.2 UJ 1.2 UJ 1.2 UJ 1.2 UJ 1.2 UJ 1 5 10 1 1 As 150 150 140 110 160 218 228 195 199 167 12 14 0 U 12 14 15 14 63 72 54 63 34 64 73 27 31 27 31 24 80 53 65 64 99 Cd 6.6 6.3 6.1 5 6.8 0.5 U 0.5 U 0.1 U 0.5 U 0.56 0.52 U 0.57 U 10 11 30 1.3 1.5 1.2 1.5 1.1 51 12 Cr 120 120 120 92 130 57 41 92 100 0 U 91 110 110 110 48 70 80 88 51 118 70 93 100 90 100 91 106 80 73 41 Cu 270 260 250 200 280 212 202 176 200 186 81 110 0.2 U 82 95 100 95 56 52 72 67 75 59 55 200 220 190 220 180 210 211 228 200 209 Fe 42,000 42,000 40,000 32,000 44,000 30,708 30,725 26,884 27,483 29,383 17,000 20,000 4 J 17,000 19,000 21,000 19,000 15,548 16,025 16,718 15,862 17,031 16,455 16,043 17,000 18,000 16,000 18,000 15,000 15,187 15,903 16,972 15,568 16,258 Pb 7 7 J+ 8 6 8 0 0 0 96 24 25 0 U 22 28 33 28 108 96 97 56 60 119 88 99 83 97 75 188 204 197 178 219 Hg 2.8 1.5 J- 1.5 1.4 21 0.091 U 0.099 U 2.4 0.081 U 0.084 U 0.084 U 0.084 U 7 7 4 8 4 86 0.48 0.57 0.41 0.43 0.42 9 7 8 Ni 870 860 830 660 910 608 636 508 567 551 180 210 2 U 180 210 220 210 132 135 155 124 165 141 144 150 160 140 170 140 117 116 123 117 118 D-23 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 38 38 38 38 38 38 38 38 38 38 39 39 39 39 39 39 39 39 39 39 39 39 39 39 40 40 40 40 40 40 40 40 40 40 Sample ID LV-SE-ll-XX LV-SE-29-XX LV-SE-44-XX LV-SE-46-XX LV-SE-52-XX LV-SE-11-XC LV-SE-29-XC LV-SE-44-XC LV-SE-46-XC LV-SE-52-XC RF-SE-07-XX RF-SE-12-XX RF-SE-23-XX RF-SE-36-XX RF-SE-42-XX RF-SE-45-XX RF-SE-53-XX RF-SE-07-XC RF-SE-12-XC RF-SE-23-XC RF-SE-36-XC RF-SE-42-XC RF-SE-45-XC RF-SE-53-XC RF-SE-03-XX RF-SE-28-XX RF-SE-38-XX RF-SE-49-XX RF-SE-55-XX RF-SE-03-XC RF-SE-28-XC RF-SE-38-XC RF-SE-49-XC RF-SE-55-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 870 860 830 660 910 608 636 508 567 551 180 210 2 U 180 210 220 210 132 135 155 124 165 141 144 150 160 140 170 140 117 116 123 117 118 Se 1.3 U 1.2 U 1.4 U 0.88 U 1.4 U 1.3 U 1.2 U 0.25 U 1 U 1.3 U 1.3 U 1.3 U 6 14 1.2 U 1.2 U 1.2 U 1.2 U 1.2 U Ag 1.4 U 1.4 U 1.4 U 0.88 U 1.4 U 7 0 0 1.3 U 1.2 U 0.37 1.2 U 1.3 U 1.3 U 1.3 U 25 4 4 14 3 1.2 U 1.2 U 1.2 U 1.2 U 1.2 U 6 3 8 V 35 35 34 27 38 0 0 0 0 61 34 38 3 U 34 40 43 40 0 35 49 0 33 0 26 40 44 39 43 35 42 61 0 9 0 Zn 200 200 190 150 210 191 202 202 189 187 130 140 1 U 120 140 150 140 171 190 219 227 248 217 185 300 320 300 330 280 481 486 552 530 534 D-24 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 41 41 41 41 41 41 41 41 41 41 42 42 42 42 42 42 42 42 42 42 43 43 43 43 43 43 43 43 43 43 Sample ID RF-SE-06-XX RF-SE-13-XX RF-SE-27-XX RF-SE-31-XX RF-SE-58-XX RF-SE-06-XC RF-SE-13-XC RF-SE-27-XC RF-SE-31-XC RF-SE-58-XC RF-SE-02-XX RF-SE-22-XX RF-SE-25-XX RF-SE-30-XX RF-SE-57-XX RF-SE-02-XC RF-SE-22-XC RF-SE-25-XC RF-SE-30-XC RF-SE-57-XC RF-SE-15-XX RF-SE-24-XX RF-SE-32-XX RF-SE-43-XX RF-SE-59-XX RF-SE-15-XC RF-SE-24-XC RF-SE-32-XC RF-SE-43-XC RF-SE-59-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 2 7 2 6 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 2 10 2 7 2 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 1.3 UJ 6 3 3 10 12 As 70 76 64 39 71 96 92 92 123 89 110 99 88 89 89 143 179 107 125 123 120 130 J+ 120 130 140 180 207 148 168 152 Cd 3.6 3.7 3.1 1.8 3.6 22 2 5.4 4.7 4 4.3 4.5 4 22 25 6.2 6.5 J+ 5.1 5.7 5.9 21 38 Cr 90 92 78 63 89 78 97 59 93 84 78 78 79 58 79 80 101 72 74 J+ 64 68 73 49 75 36 Cu 490 530 440 250 500 468 485 485 523 520 740 670 580 610 610 599 649 649 637 637 820 860 J+ 770 840 890 887 889 901 938 928 Fe 20,000 21,000 18,000 12,000 21,000 16,459 16,918 17,224 17,807 17,583 24,000 22,000 19,000 21,000 21,000 17,633 17,877 18,000 18,543 17,762 23,000 24,000 J+ 20,000 22,000 23,000 19,197 19,447 19,415 19,857 19,383 Pb 230 230 200 120 230 356 452 381 392 501 330 300 270 290 300 478 467 497 542 505 390 410 J+ 330 350 380 661 654 703 678 686 Hg l.l 1.2 1.2 1.1 1.2 5 1.6 1.7 1.5 1.5 1.5 7 2.6 2.3 2.8 2.7 0.085 U 8 D-25 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 41 41 41 41 41 41 41 41 41 41 42 42 42 42 42 42 42 42 42 42 43 43 43 43 43 43 43 43 43 43 Sample ID RF-SE-06-XX RF-SE-13-XX RF-SE-27-XX RF-SE-31-XX RF-SE-58-XX RF-SE-06-XC RF-SE-13-XC RF-SE-27-XC RF-SE-31-XC RF-SE-58-XC RF-SE-02-XX RF-SE-22-XX RF-SE-25-XX RF-SE-30-XX RF-SE-57-XX RF-SE-02-XC RF-SE-22-XC RF-SE-25-XC RF-SE-30-XC RF-SE-57-XC RF-SE-15-XX RF-SE-24-XX RF-SE-32-XX RF-SE-43-XX RF-SE-59-XX RF-SE-15-XC RF-SE-24-XC RF-SE-32-XC RF-SE-43-XC RF-SE-59-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 150 160 130 86 150 108 122 100 115 107 180 160 140 150 150 105 150 140 131 112 160 170 J+ 140 150 160 125 140 127 127 136 Se 1.3 U 1.3 U 1.3 U 1.3 U 1.3 U 24 1.3 U 1.3 U 1.5 1.3 U 2 4 23 1.4 1.3 U 1.3 U 1.3 U 1.3 U 14 Ag 1.3 U 1.3 1.3 U 1.3 U 1.3 U 24 22 5 25 2.7 2.3 1.7 1.9 2.2 9 10 3 3.6 3.8 J+ 4.2 4 4.5 4 16 19 22 V 44 45 39 28 46 50 0 14 33 23 50 44 40 44 44 0 0 0 0 0 45 46 J+ 36 40 42 0 22 0 40 48 Zn 740 790 670 420 770 1,092 1,173 1,090 1,156 1,231 1,100 990 890 960 1,000 1,295 1,445 1,371 1,452 1,465 1,300 1,400 J- 1,100 1,200 1,300 1,768 1,861 1,857 1,939 1,868 D-26 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 44 44 44 44 44 44 44 44 44 44 45 45 45 45 45 45 45 45 45 45 46 46 46 46 46 46 47 47 47 47 47 47 Sample ID RF-SE-05-XX RF-SE-26-XX RF-SE-39-XX RF-SE-44-XX RF-SE-56-XX RF-SE-05-XC RF-SE-26-XC RF-SE-39-XC RF-SE-44-XC RF-SE-56-XC RF-SE-04-XX RF-SE-14-XX RF-SE-19-XX RF-SE-34-XX RF-SE-52-XX RF-SE-04-XC RF-SE-14-XC RF-SE-19-XC RF-SE-34-XC RF-SE-52-XC BN-SO-11-XX BN-SO-14-XX BN-SO-23-XX BN-SO-11-XC BN-SO-14-XC BN-SO-23-XC BN-SO-09-XX BN-SO-12-XX BN-SO-24-XX BN-SO-09-XC BN-SO-12-XC BN-SO-24-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 4.1 J+ 2.2 J+ 2.9 J+ 2.7 J+ 3.5 J+ 3 9 12 7 12 3.2 J+ 4.4 J+ 3.7 J+ 2.9 J+ 3.4 J+ 4 5 15 17 16 4 J- 3.5 J- 1.2 UJ 5 8 0 750 J- 750 J- 810 J- 374 366 348 As 160 140 160 140 180 163 225 209 231 212 230 260 250 210 220 303 274 284 343 311 2,900 2,800 2,800 4,644 4,470 4,327 97 89 97 60 52 70 Cd 9.1 8.4 9.3 8.2 9.6 15 30 24 12 12 13 10 11 27 12 25 720 690 700 951 850 818 2,700 2,600 2,900 3,128 3,078 2,870 Cr 69 64 73 64 75 40 43 86 46 45 42 47 48 39 42 51 47 49 820 800 800 519 507 533 2,900 2,800 3,000 1,613 1,605 1,563 Cu 1,000 990 1,100 970 1200 1,115 1,133 1,157 1,171 1,138 1,500 1,700 1,700 1,400 1,500 1,637 1,635 1,673 1,727 1,720 120 120 120 431 406 423 100 96 100 76 67 75 Fe 26,000 23,000 26,000 24,000 27,000 20,304 20,882 21,647 21,394 20,900 27,000 30,000 30,000 24,000 26,000 22,522 23,684 22,966 23,564 23,725 23,000 22,000 23,000 24,935 24,994 25,464 22,000 21,000 23,000 15,548 15,511 15,803 Pb 450 440 490 420 490 729 683 769 657 694 730 800 800 660 720 1,023 1,118 1,145 1,069 56 51 52 0 61 77 4,700 4,500 4,900 7,409 7,237 7,395 Hg 2.6 2.5 2.2 2.3 2.2 7 5 4.2 4.7 3.9 4.5 4.1 1,100 24 J- 26 31 25 43 37 0.39 0.34 0.37 D-27 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 44 44 44 44 44 44 44 44 44 44 45 45 45 45 45 45 45 45 45 45 46 46 46 46 46 46 47 47 47 47 47 47 Sample ID RF-SE-05-XX RF-SE-26-XX RF-SE-39-XX RF-SE-44-XX RF-SE-56-XX RF-SE-05-XC RF-SE-26-XC RF-SE-39-XC RF-SE-44-XC RF-SE-56-XC RF-SE-04-XX RF-SE-14-XX RF-SE-19-XX RF-SE-34-XX RF-SE-52-XX RF-SE-04-XC RF-SE-14-XC RF-SE-19-XC RF-SE-34-XC RF-SE-52-XC BN-SO-11-XX BN-SO-14-XX BN-SO-23-XX BN-SO-11-XC BN-SO-14-XC BN-SO-23-XC BN-SO-09-XX BN-SO-12-XX BN-SO-24-XX BN-SO-09-XC BN-SO-12-XC BN-SO-24-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 150 140 150 140 160 105 107 94 107 112 130 140 140 120 130 117 105 126 125 137 2,900 2,800 2,800 2,533 2,429 2,460 1,500 1,400 1,600 1,158 1,194 1,169 Se 3.1 2.8 2.6 2.4 1.8 1 2.8 3 4.1 1.9 2 140 130 130 260 208 206 290 290 300 717 624 611 Ag 7.4 J- 7.2 J- 8.2 J- 7.2 J- 8.3 J- 11 17 6 7 12 J- 13 J- 14 J- 10 J- 11 J- 42 25 33 12 9 140 J- 140 J- 130 J- 166 142 135 100 J- 210 J- 140 J- 520 512 447 V 48 42 49 44 51 50 0 12 0 40 46 51 52 42 47 48 34 0 0 0 150 150 150 48 75 76 340 310 350 99 40 75 Zn 1,800 1,700 1,900 1,600 1,900 2,313 2,307 2,279 2,351 2,222 2,400 2,600 2,700 2,200 2,300 2,884 3,004 2,922 2,971 2,916 3,900 3,800 3,800 5,392 5,294 5,306 81 74 81 104 110 116 D-28 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 48 48 48 48 48 48 49 49 49 49 49 49 50 50 50 50 50 50 51 51 51 51 51 51 52 52 52 52 52 52 53 53 53 53 53 53 Sample ID SB-SO-09-XX SB-SO-20-XX SB-SO-31-XX SB-SO-09-XC SB-SO-20-XC SB-SO-31-XC SB-SO-29-XX SB-SO-36-XX SB-SO-56-XX SB-SO-29-XC SB-SO-36-XC SB-SO-56-XC SB-SO-04-XX SB-SO-34-XX SB-SO-49-XX SB-SO-04-XC SB-SO-34-XC SB-SO-49-XC WS-SO-07-XX WS-SO-11-XX WS-SO-25-XX WS-SO-07-XC WS-SO-11-XC WS-SO-25-XC WS-SO-10-XX WS-SO-20-XX WS-SO-23-XX WS-SO-10-XC WS-SO-20-XC WS-SO-23-XC AS-SO-03-XX AS-SO-05-XX AS-SO-08-XX AS-SO-03-XC AS-SO-05-XC AS-SO-08-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 1.3 UJ 1.3 UJ 1.3 UJ 3 11 0 1.2 U 1.2 U 1.2 U 0 0 0 940 980 700 522 528 3.8 1.2 U 1.2 U 16 17 13 1.3 U 1.3 U 1.3 U 22 23 21 1.2 U 1.2 U 1.2 U 4 1 1 As 9 11 8 J- 67 62 68 9 8 10 74 52 95 13 12 12 121 121 85 53 46 59 95 138 44 83 100 110 80 56 44 14 9 10 101 67 55 Cd 0.51 U 0.51 U 0.51 U 10 13 0.5 U 0.5 U 0.5 U 9 28 17 2,800 2,500 2,500 3,100 2,907 3,174 1.9 1.4 3.1 1.8 1.9 2.1 11 40 50 1,300 900 930 1,167 1,184 1,217 Cr 130 170 140 160 64 104 140 120 150 75 150 144 2,800 2,500 2,400 1,800 1,691 1,770 640 570 730 499 476 379 67 81 82 93 52 80 33 23 24 59 Cu 120 150 130 414 379 393 130 100 140 408 424 419 100 91 89 80 72 71 4,400 3,900 4,900 9,740 9,332 6,663 76 90 96 286 288 271 6,200 4,500 4,600 8,843 9,977 9,488 Fe 35,000 44,000 38,000 38,474 32,246 35,657 41,000 33,000 42,000 36,179 37,462 38,650 38,000 34,000 33,000 24,853 23,843 24,585 25,000 19,000 24,000 20,630 19,876 16,469 19,000 23,000 23,000 26,434 25,411 24,797 15,000 11,000 11,000 11,957 12,322 12,255 Pb 19 24 21 32 0 0 19 15 20 41 55 40 21 18 18 68 20 51 1,700 1,500 1,900 5,119 4,887 3,193 1,900 2,300 2,500 5,426 4,817 4,721 160 110 120 208 211 218 Hg 30 10 32 34 7.9 J 36 9 15 19 26 40 36 36 34 484 44 0.26 0.27 0.25 9 0.058 U 0.06 U 0.05 U 20 18 3.7 J- 2.5 J- 2.5 J- 5 D-29 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 48 48 48 48 48 48 49 49 49 49 49 49 50 50 50 50 50 50 51 51 51 51 51 51 52 52 52 52 52 52 53 53 53 53 53 53 Sample ID SB-SO-09-XX SB-SO-20-XX SB-SO-31-XX SB-SO-09-XC SB-SO-20-XC SB-SO-31-XC SB-SO-29-XX SB-SO-36-XX SB-SO-56-XX SB-SO-29-XC SB-SO-36-XC SB-SO-56-XC SB-SO-04-XX SB-SO-34-XX SB-SO-49-XX SB-SO-04-XC SB-SO-34-XC SB-SO-49-XC WS-SO-07-XX WS-SO-11-XX WS-SO-25-XX WS-SO-07-XC WS-SO-11-XC WS-SO-25-XC WS-SO-10-XX WS-SO-20-XX WS-SO-23-XX WS-SO-10-XC WS-SO-20-XC WS-SO-23-XC AS-SO-03-XX AS-SO-05-XX AS-SO-08-XX AS-SO-03-XC AS-SO-05-XC AS-SO-08-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 2900 3700 3200 J- 2,715 2,375 2,499 200 160 210 146 166 169 3,300 3,000 2,800 2,718 2,565 2,648 260 240 300 437 420 310 290 350 380 328 312 319 520 370 380 607 675 605 Se 26 30 28 J- 28 31 21 160 130 160 381 369 383 390 360 330 912 855 960 1.2 U 1.2 U 1.2 U 9 280 340 360 1,175 998 1,017 200 140 140 334 307 339 Ag 160 J- 140 J- 160 J- 387 300 335 1.2 UJ 1.2 UJ 1.2 UJ 3 4 5 1.3 UJ 1.3 UJ 1.2 UJ 65 400 J- 340 J- 450 J- 542 537 378 1.3 UJ 1.3 UJ 1.3 UJ 19 8 16 480 J- 330 J- 280 J- 366 544 377 V 120 160 140 41 0 144 400 320 410 199 225 97 58 52 52 0 76 96 48 43 54 39 9 0 260 320 330 151 106 117 29 23 23 13 0 0 Zn 3,600 4,500 3,900 J- 4,097 3,934 4,005 3,900 3,200 4,100 4,175 4,103 4,111 86 77 72 70 62 63 180 160 200 306 327 279 1,900 2,300 2,500 3,742 3,763 3,736 350 250 260 532 599 556 D-30 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 54 54 54 54 54 54 55 55 55 55 55 55 56 56 56 56 56 56 57 57 57 57 57 57 58 58 58 58 58 58 59 59 59 59 59 59 Sample ID LV-SO-03-XX LV-SO-40-XX LV-SO-49-XX LV-SO-03-XC LV-SO-40-XC LV-SO-49-XC LV-SO-04-XX LV-SO-34-XX LV-SO-37-XX LV-SO-04-XC LV-SO-34-XC LV-SO-37-XC CN-SO-03-XX CN-SO-06-XX CN-SO-07-XX CN-SO-03-XC CN-SO-06-XC CN-SO-07-XC CN-SO-02-XX CN-SO-05-XX CN-SO-09-XX CN-SO-02-XC CN-SO-05-XC CN-SO-09-XC LV-SE-06-XX LV-SE-13-XX LV-SE-41-XX LV-SE-06-XC LV-SE-13-XC LV-SE-41-XC LV-SE-05-XX LV-SE-20-XX LV-SE-43-XX LV-SE-05-XC LV-SE-20-XC LV-SE-43-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 1.6 2.7 7.4 6 4 1 860 870 J- 590 347 335 344 22 20 20 11 12 8 230 130 120 74 78 78 30 31 30 40 38 45 92 140 J+ 160 J+ 90 93 103 As 42 42 43 61 75 65 120 110 J- 84 90 52 39 87 91 90 169 201 163 19 6 6 79 80 51 23 24 21 87 54 74 20 31 24 93 74 59 Cd 590 580 600 670 730 604 2,400 2,300 J- 1,700 3,054 2,985 3,095 63 64 63 77 68 94 820 630 580 677 695 667 160 160 150 269 234 235 440 680 550 657 745 743 Cr 600 590 610 346 393 346 2,300 2,200 J- 1,600 1,351 1,443 1,423 17 18 19 290 26 21 38 35 540 540 480 341 379 365 840 1,400 1,100 652 714 709 Cu 130 130 130 451 449 413 98 87 66 61 48 72 72 74 72 93 82 93 140 160 140 336 308 296 30 30 26 3 4 16 39 60 47 225 231 233 Fe 24,000 24,000 25,000 34,877 35,004 30,730 22,000 20,000 J- 16,000 20,656 20,387 20,591 15,000 16,000 17,000 16,552 15,546 17,267 22,000 23,000 19,000 22,137 20,389 20,290 18,000 18,000 16,000 17,343 17,202 18,059 16,000 22,000 19,000 25,232 24,839 24,954 Pb 94 92 98 173 153 197 4,000 3,700 J- 2,800 8,958 8,837 8,918 130 130 130 272 256 294 490 25 23 0 0 43 1,600 1,600 1,500 3,778 3,596 3,754 14 21 17 101 63 107 Hg 48 J- 46 J- 52 J- 13 130 J- 130 J- 130 J- 37 38 21 34 J- 40 J- 36 J- 10 7 15 270 J- 280 J- 260 J- 98 110 98 610 J- 640 J- 610 J- 245 225 249 2.6 J- 2.8 2.8 8 D-31 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 54 54 54 54 54 54 55 55 55 55 55 55 56 56 56 56 56 56 57 57 57 57 57 57 58 58 58 58 58 58 59 59 59 59 59 59 Sample ID LV-SO-03-XX LV-SO-40-XX LV-SO-49-XX LV-SO-03-XC LV-SO-40-XC LV-SO-49-XC LV-SO-04-XX LV-SO-34-XX LV-SO-37-XX LV-SO-04-XC LV-SO-34-XC LV-SO-37-XC CN-SO-03-XX CN-SO-06-XX CN-SO-07-XX CN-SO-03-XC CN-SO-06-XC CN-SO-07-XC CN-SO-02-XX CN-SO-05-XX CN-SO-09-XX CN-SO-02-XC CN-SO-05-XC CN-SO-09-XC LV-SE-06-XX LV-SE-13-XX LV-SE-41-XX LV-SE-06-XC LV-SE-13-XC LV-SE-41-XC LV-SE-05-XX LV-SE-20-XX LV-SE-43-XX LV-SE-05-XC LV-SE-20-XC LV-SE-43-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni Se Ag V Zn 2,000 120 210 J- 120 3,700 1,900 120 210 J- 120 3,700 2,000 120 220 J- 120 3,800 1,795 320 204 41 4,677 1,815 291 223 99 4,664 1,650 270 191 81 4,653 2,000 230 1.2 UJ 260 53 1,900 J- 220 J- 1.2 UJ 230 J- 48 J- 1,400 170 1.2 U 180 37 1,834 502 107 57 1,791 549 19 105 38 1,875 586 22 133 63 74 36 90 30 58 76 38 94 32 59 75 37 91 33 58 81 22 114 33 132 78 46 99 23 140 102 41 108 29 140 530 190 68 160 1,900 360 190 78 160 2,200 330 170 74 140 2,100 327 406 82 75 3,552 308 385 73 67 3,580 289 388 92 78 3,451 360 160 110 480 52 360 160 110 470 51 320 150 99 420 46 299 406 148 194 64 305 343 139 207 79 331 329 139 217 64 400 340 49 340 1,800 660 500 75 J- 530 2,800 530 420 60 J- 430 2,300 411 1,189 65 151 3,269 427 1,255 74 211 3,354 420 1,210 77 173 3,300 D-32 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 60 60 60 60 60 60 61 61 61 61 61 61 62 62 62 62 62 62 63 63 63 63 63 63 64 64 64 64 64 64 Sample ID LV-SE-15-XX LV-SE-17-XX LV-SE-51-XX LV-SE-15-XC LV-SE-17-XC LV-SE-51-XC TL-SE-05-XX TL-SE-09-XX TL-SE-13-XX TL-SE-05-XC TL-SE-09-XC TL-SE-13-XC TL-SE-06-XX TL-SE-17-XX TL-SE-28-XX TL-SE-06-XC TL-SE-17-XC TL-SE-28-XC TL-SE-07-XX TL-SE-21-XX TL-SE-30-XX TL-SE-07-XC TL-SE-21-XC TL-SE-30-XC TL-SE-02-XX TL-SE-08-XX TL-SE-16-XX TL-SE-02-XC TL-SE-08-XC TL-SE-16-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 290 J+ 280 J+ 210 J+ 150 152 119 100 J+ 100 J+ 95 J+ 134 128 125 1.2 U 1.2 U 1.2 U 16 17 21 30 33 31 48 50 52 77 66 73 101 123 120 As 32 31 26 70 72 129 34 33 31 53 65 87 86 85 89 67 63 126 11 13 11 74 69 54 15 10 15 55 71 33 Cd 1,300 1,300 1,100 1,365 1,362 1,186 0.34 J 0.24 J 0.45 J 350 340 360 463 501 520 48 51 47 58 42 44 160 180 170 159 214 213 Cr 83 79 72 69 45 40 39 36 J+ 34 33 34 20 66 73 64 16 13 64 74 69 43 12 Cu 2,300 2,200 2,000 2,440 2,459 2,275 4,900 4,800 4,400 J+ 6,233 6,272 6,013 2000 2100 2100 2,895 2,729 2,659 2200 2300 2200 3,700 3,736 3,573 3,100 3,200 3,100 4,258 5,452 5,324 Fe 22,000 21,000 19,000 18,435 18,517 17,652 24,000 23,000 22,000 J+ 22,153 21,976 22,026 22,000 21,000 22,000 22,639 21,993 21,638 37,000 44,000 36,000 53,232 53,772 52,769 32,000 45,000 38,000 45,180 54,821 52,189 Pb 18 17 J- 15 47 80 0 1,200 1,200 1,100 J+ 2,327 2,295 2,354 1,700 1,700 1,700 4,143 4,379 4,711 13 15 14 73 117 129 12 11 13 144 73 43 Hg 500 490 470 247 236 212 980 820 990 424 434 450 2.2 2.6 2.8 40 120 100 41 19 23 400 350 420 152 163 192 D-33 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 60 60 60 60 60 60 61 61 61 61 61 61 62 62 62 62 62 62 63 63 63 63 63 63 64 64 64 64 64 64 Sample ID LV-SE-15-XX LV-SE-17-XX LV-SE-51-XX LV-SE-15-XC LV-SE-17-XC LV-SE-51-XC TL-SE-05-XX TL-SE-09-XX TL-SE-13-XX TL-SE-05-XC TL-SE-09-XC TL-SE-13-XC TL-SE-06-XX TL-SE-17-XX TL-SE-28-XX TL-SE-06-XC TL-SE-17-XC TL-SE-28-XC TL-SE-07-XX TL-SE-21-XX TL-SE-30-XX TL-SE-07-XC TL-SE-21-XC TL-SE-30-XC TL-SE-02-XX TL-SE-08-XX TL-SE-16-XX TL-SE-02-XC TL-SE-08-XC TL-SE-16-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 230 220 200 187 184 166 54 53 49 116 120 103 44 43 44 90 71 65 94 100 93 152 118 122 99 100 100 181 155 176 Se 92 89 76 76 95 70 130 130 120 190 216 180 45 44 45 83 31 50 120 140 120 404 421 483 44 39 44 77 92 66 Ag 300 J- 200 J- 250 J- 513 577 437 180 J- 170 J- 160 J 224 254 227 56 56 57 86 85 89 63 67 62 117 99 130 120 130 120 171 227 227 V 180 170 160 94 127 69 66 63 59 J+ 0 0 0 78 78 81 0 0 13 110 120 100 0 0 58 110 120 110 65 0 0 Zn 62 58 54 27 53 0 100 100 96 86 104 99 83 81 83 105 116 117 160 170 160 95 94 115 160 170 160 91 93 91 D-34 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 65 65 65 65 65 65 65 65 65 65 65 65 65 65 66 66 66 66 66 66 67 67 67 67 67 67 68 68 68 68 68 68 Sample ID RF-SE-01-XX RF-SE-09-XX RF-SE-11-XX RF-SE-17-XX RF-SE-29-XX RF-SE-37-XX RF-SE-50-XX RF-SE-01-XC RF-SE-09-XC RF-SE-11-XC RF-SE-17-XC RF-SE-29-XC RF-SE-37-XC RF-SE-50-XC RF-SE-08-XX RF-SE-10-XX RF-SE-33-XX RF-SE-08-XC RF-SE-10-XC RF-SE-33-XC RF-SE-16-XX RF-SE-41-XX RF-SE-48-XX RF-SE-16-XC RF-SE-41-XC RF-SE-48-XC RF-SE-18-XX RF-SE-35-XX RF-SE-54-XX RF-SE-18-XC RF-SE-35-XC RF-SE-54-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb 12 10 11 11 13 11 8.9 8 11 10 11 0 0 4 14 12 13 21 21 19 85 J- 100 100 52 52 57 320 300 320 160 164 165 As 230 260 240 250 280 260 230 406 424 433 406 418 447 437 460 400 440 737 784 709 72 J- 82 87 114 109 142 810 740 880 1,208 1,239 1,238 Cd 40 45 43 43 49 45 40 49 69 52 59 69 66 62 67 58 64 65 75 73 310 J- 360 380 421 463 432 770 700 840 899 942 918 Cr 280 310 300 300 330 320 280 158 232 213 270 192 219 219 510 440 490 337 355 324 820 J- 950 1,000 664 617 640 950 860 1,000 615 681 621 Cu 63 71 72 67 75 72 65 205 216 209 220 212 216 211 1,800 1,500 1,700 2,066 2,205 2,138 73 J- 85 90 112 97 104 78 70 86 30 44 37 Fe 14,000 16,000 15,000 15,000 17,000 16,000 14,000 15,474 15,814 15,982 16,378 16,296 16,332 16,381 18,000 16,000 18,000 12,810 13,872 13,548 16,000 J- 18,000 19,000 14,873 14,638 14,899 16,000 15,000 18,000 11,932 12,298 12,444 Pb 22 26 25 26 26 27 23 33 77 27 82 70 32 37 580 510 570 1,023 987 1,068 24 J- 25 27 44 74 36 860 780 920 1,267 1,329 1,346 Hg 47 45 52 20 20 22 19 7 19 7 16 17 6 14 29 27 28 16 8 11 260 230 250 102 107 111 600 650 670 221 242 243 D-35 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 65 65 65 65 65 65 65 65 65 65 65 65 65 65 66 66 66 66 66 66 67 67 67 67 67 67 68 68 68 68 68 68 Sample ID RF-SE-01-XX RF-SE-09-XX RF-SE-11-XX RF-SE-17-XX RF-SE-29-XX RF-SE-37-XX RF-SE-50-XX RF-SE-01-XC RF-SE-09-XC RF-SE-11-XC RF-SE-17-XC RF-SE-29-XC RF-SE-37-XC RF-SE-50-XC RF-SE-08-XX RF-SE-10-XX RF-SE-33-XX RF-SE-08-XC RF-SE-10-XC RF-SE-33-XC RF-SE-16-XX RF-SE-41-XX RF-SE-48-XX RF-SE-16-XC RF-SE-41-XC RF-SE-48-XC RF-SE-18-XX RF-SE-35-XX RF-SE-54-XX RF-SE-18-XC RF-SE-35-XC RF-SE-54-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni 200 220 210 210 240 220 200 169 182 192 189 186 178 183 250 220 240 233 252 247 1,700 J- 1,900 2,000 1,663 1,618 1,608 390 350 420 276 340 307 Se 21 23 20 22 26 23 20 31 59 42 39 41 28 6 1.2 U 1.2 U 2.2 140 140 160 265 257 268 Ag 37 42 40 40 44 44 38 46 42 27 49 62 43 52 0.39 U 0.34 U 0.33 U 13 5 130 J- 140 150 156 166 169 140 150 180 258 268 260 V 29 32 29 30 35 32 29 0 48 0 0 0 0 0 120 100 120 59 61 37 32 J- 39 40 21 0 54 390 340 410 142 142 132 Zn 1,700 1,900 1,800 1,800 2,100 1,900 1,700 3,293 3,500 3,405 3,473 3,421 3,423 3,463 120 110 130 81 107 105 760 J- 830 880 1,373 1,401 1,377 120 110 120 164 176 153 D-36 ------- Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 69 69 69 69 69 69 70 70 70 70 70 70 Sample ID RF-SE-20-XX RF-SE-46-XX RF-SE-51-XX RF-SE-20-XC RF-SE-46-XC RF-SE-51-XC RF-SE-21-XX RF-SE-40-XX RF-SE-47-XX RF-SE-21-XC RF-SE-40-XC RF-SE-47-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Sb As Cd Cr Cu Fe Pb Hg 550 1300 540 94 93 20,000 28 0.48 270 590 240 44 40 8,900 13 0.45 480 1100 450 77 77 17,000 23 0.48 219 1,760 576 43 144 16,036 13 232 1,858 619 73 139 16,115 89 19 232 1,774 595 76 136 16,229 76 12 1.3 U 62 1,700 76 1,000 16,000 2,100 320 1.3 U 70 1,900 85 1,100 18,000 2,400 280 1.3 U 72 1,900 90 1,200 19,000 2,400 320 19 85 2,180 50 1,060 13,404 3,814 95 20 122 2,314 91 1,101 13,281 3,973 93 19 116 2,295 53 1,093 13,555 3,841 92 Appendix D. Analytical Data Summary, Xcalibur ElvaX and Reference Laboratory (Continued) Blend No. 69 69 69 69 69 69 70 70 70 70 70 70 Sample ID RF-SE-20-XX RF-SE-46-XX RF-SE-51-XX RF-SE-20-XC RF-SE-46-XC RF-SE-51-XC RF-SE-21-XX RF-SE-40-XX RF-SE-47-XX RF-SE-21-XC RF-SE-40-XC RF-SE-47-XC Source of Data Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Reference Laboratory Reference Laboratory Reference Laboratory Xcalibur XRF Services Xcalibur XRF Services Xcalibur XRF Services Ni Se Ag V Zn 1,400 380 59 36 1,400 650 170 26 16 650 1,200 320 48 30 1,200 1,079 828 80 0 2,094 1,056 912 69 0 2,115 1,075 818 84 0 2,054 220 440 120 130 100 250 480 100 150 120 250 510 120 150 120 179 1,232 305 58 107 193 1,299 325 52 61 211 1,321 312 59 117 Notes: All concentrations reported in milligrams per kilogram (mg/kg), or parts per million (ppm). Sample results for which "0" or no value was reported were considered nondetections as reported by Xcalibur. Reference laboratory data qualifiers were as follows: J Estimated concentration. J+ Concentration is considered estimated and biased high. J- Concentration is considered estimated and biased low. U Analyte is not detected; the associated concentration value is the sample reporting limit. D-37 ------- APPENDIX E STATISTICAL DATA SUMMARIES ------- 1000 -i QOO onn ฃ700 p* & X "a 500 - s b 400 - ฃ a 2 300 - X 200 100 i .1 0 Figure E-l : Linear Correlation Plot for Antimony Xcalibur ElvaX vs Reference Laboratory A Xcalibur ElvaX vs Certified Value / T . ,v ... . v T , y) / 1 / y = 0.44x + 50.81 y = 0.15x + 19.40 R2 = 083 R2 = 0.98 / / ^'^ ~/\ ^ ^ ^A 1 "/ ^ '^' ^^^^^^ &~^ 500 1000 1500 2000 2500 3000 3500 Reference Laboratory or Certified Value (ppm) 7000 6000 ^ 5000 & X 4000 X ซ _^ ซ 3000 5 a 03 * 2000 1000 0 Figure E-2: Linear Correlation Plot for Arsenic Xcalibur ElvaX 45 Degrees _ y = 1.23x + 35.0(! R2 = 0 97 s s ^''^ s ^^ s .^ s ^^ s<^^ * s'2' *s*s^_ ^ 3 1000 2000 3000 4000 5000 6000 Reference Laboratory (ppm) E-l ------- Figure E-3: Linear Correlation Plot for Cadmium 3500 3000 2500 - 2000 - 1500 - a ra 1000 - 500 Xcalibur ElvaX 45 Degrees Linear (Xcalibur ElvaX) 500 1000 1500 2000 Reference Laboratory (ppm) 500 3000 Figure E-4: Linear Correlation Plot for Chromium 3500 3000 2500 - <& 2000 ~ 1500 3 a * 1000 - 500 Xcalibur ElvaX 45 Degrees Linear (Xcalibur ElvaX) y = 0.62x + 34.93 R2 = 0.98 500 1000 1500 2000 Reference Laboratory (ppm) 2500 3000 3500 E-2 ------- Figure E-5: Linear Correlation Plot for Copper 10000 9000 8000 41 X X 7000 6000 5000 4000 3000 2000 1000 Xcalibur ElvaX 45 Degrees Linear (Xcalibur ElvaX) y = 1.59x-212.59 R2 = 0.93 1000 2000 3000 4000 Reference Laboratory (ppm) 5000 6000 Figure E-6: Linear Correlation Plot for Iron Xcalibur ElvaX 45 Degrees Linear (Xcalibur ElvaX) y = 0.67x +5071.90 R2 = 0.93 20000 40000 60000 80000 100000 120000 140000 160000 180000 200000 Reference Laboratory (ppm) E-3 ------- Figure E-7: Linear Correlation Plot for Lead 60000 50000 - 40000 - 30000 - a ra 20000 - 10000 - Xcalibur ElvaX 45 Degrees Linear (Xcalibur ElvaX) y = 1.40x +324.06 R2 = 0.94 5000 10000 15000 20000 25000 Reference Laboratory (ppm) 30000 35000 40000 Figure E-8: Linear Correlation Plot for Mercury 9000 8000 - 7000 - 6000 - 5000 - r5 4000 - 3000 - 2000 - 1000 0 Xcalibur ElvaX 45 Degrees Linear (Xcalibur ElvaX) y = 0.19x+ 113.65 R2 = 0.82 1000 2000 3000 4000 5000 6000 Reference Laboratory (ppm) 7000 8000 9000 E-4 ------- Figure E-9: Linear Correlation Plot for Nickel 3500 3000 X X 2500 2000 1500 a ra 1000 500 Xcalibur ElvaX 45 Degrees Linear (Xcalibur ElvaX) 500 1000 1500 2000 2500 Reference Laboratory (ppm) 3000 3500 1400 1200 -- 1000 -- <& 800 -- 600 -- 400 - 200 Figure E-10: Linear Correlation Plot for Selenium Xcalibur ElvaX 45 Degrees Linear (Xcalibur ElvaX) y = 2.99x-96.99 R2 = 0.96 100 200 300 400 Reference Laboratory (ppm) 500 600 E-5 ------- Figure E-ll: Linear Correlation Plot for Silver 600 500 400 X 3 300 3 s~ - .Q 13 200 100 Xcalibur ElvaX 45 Degrees Linear (Xcalibur ElvaX) 50 100 150 200 250 300 350 400 450 Reference Laboratory (ppni) 500 450 400 Figure E-12: Linear Correlation Plot for Vanadium Xcalibur ElvaX 45 Degrees Linear (Xcalibur ElvaX) 50 100 150 200 250 300 Reference Laboratory (ppm) 350 400 450 500 E-6 ------- Figure E-13: Linear Correlation Plot for Zinc 10000 9000 8000 ^ 7000 SJt 6000 ^ 5000 I ฃ 4000 a $ 3000 2000 1000 Xcalibur ElvaX 45 Degrees Linear (Xcalibur ElvaX) y = 1.03x + 223.11 R2 = 0.85 1000 2000 3000 4000 5000 Reference Laboratory (ppin) 6000 7000 8000 E-7 ------- Box Plot for Relative Percent Difference (RPD) Xcalibur ElvaX Median; Box: 25%-75%; Whisker: Non-Outlier Range 1 OU /O 160% 3 140% re ""' > ฃ^ >" 1 90ฐ/ u o 0 '^u/ฐ fli m ฃ 2 > * o g 100% a) re re 0) -1 > | g -o 80% m S it d o> "ฃ 60% ft 0) O ill 40% 0) *- S T3 = 20% TO 0% -9DO/, i i ! 22-SB ! i i i 0 i ; 1 ! V j j 9 | i j JL i i i Up ! '! >! T '* i j i j i ! 9 i i j. | ^ * D [ j ~q j. i 0 1 21 -SB i 6-WS t <; ] + 1 F [ 1 Inl L = I - i ! i > n J c J aeltv 9 c !- : J ! ! ! _ { i i ! 47-iBN ! | 9 | ! T ! 17-iAS L i T -i 1 i 1 i t ] | J 61-iTb- Tr -. 64-i-TL 9 \ j i I 8 n 9 1 q L D Q 1 p t 1 J *f 3 JL n } * I ! ! ! ! Sb-RL As Cr Fe Hg Se V Sb-CV Cd Cu Pb Ni Ag Zn Target Element n Median D 25%-75% I Non-Outlier Range o Outliers * Extremes Notes: The "box" in each box plot presents the range of RPD values that lie between the 25th and 75th percentiles (that is, the "quartiles") of the full RPD population for each element. In essence, the box displays the "interquartile range" of RPD values. The square data point within each box represents the median RPD for the population. The "whiskers" emanating from the top and bottom of each box represent the largest and smallest data points, respectively, that are within 1.5 times the interquartile range. Values outside the whiskers are identified as outliers and extremes. Some of the more significant extremes and outliers are labeled with the associated Blend numbers and sample site abbreviations (see the footnotes of Table E-5 for definitions). Also refer to Appendix D for the results and sampling site associated with each Blend number. Figure E-14. Box and Whiskers Plot for Mean RPD Values Showing Outliers and Extremes for Target Elements, Xcalibur ElvaX Data Set. E-8 ------- Table E-l. Evaluation of Accuracy - Relative Percent Difference versus Reference Laboratory Data Calculated for the Xcalibur ElvaX Matrix Soil Cone Range Level 1 Level 2 Level 3 Level 4 All Soil Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Antimony RefLab 9 2.6% 105.4% 43.7% 47.0% 5 10.2% 70.2% 32.2% 31.7% o 3 43.9% 77.4% 64.4% 71.9% ~ ~ ~ 17 2.6% 105.4% 44.0% 43.9% ERA Spike 1 154.4% 154.4% 154.4% 154.4% 1 6.2% 6.2% 6.2% 6.2% 2 0.7% 6.3% 3.5% 3.5% ~ ~ ~ 4 0.7% 154.4% 41.9% 6.2% Arsenic 15 33.7% 163.0% 62.6% 53.8% 4 8.4% 22.2% 15.6% 15.9% 4 8.4% 45.0% 23.4% 20.1% ~ ~ ~ 23 8.4% 163.0% 47.6% 45.0% Cadmium 7 0.2% 29.4% 17.3% 16.4% 7 0.4% 35.2% 13.5% 12.4% 2 10.1% 16.3% 13.2% 13.2% ~ ~ ~ 16 0.2% 35.2% 15.1% 13.9% Chromium 23 2.3% 87.2% 28.4% 21.2% 4 35.6% 49.6% 41.2% 39.9% 2 37.6% 58.1% 47.9% 47.9% ~ ~ ~ 29 2.3% 87.2% 31.5% 29.4% Copper 16 9.9% 111.1% 61.2% 62.7% 8 1.3% 15.7% 7.0% 5.7% 2 59.7% 64.4% 62.0% 62.0% ~ ~ ~ 26 1.3% 111.1% 44.6% 26.6% Iron 5 0.3% 46.2% 24.7% 25.5% 13 1.1% 33.9% 13.8% 10.3% 13 2.1% 40.3% 24.6% 29.1% 7 18.9% 43.6% 28.5% 30.9% 38 0.3% 46.2% 21.6% 24.1% Lead 7 8.3% 75.3% 51.3% 50.5% 4 0.5% 88.5% 40.4% 36.2% 8 2.2% 87.1% 50.9% 55.5% 5 5.0% 62.3% 29.6% 22.3% 24 0.5% 88.5% 44.8% 47.0% Mercury 5 26.6% 133.5% 99.0% 107.9% 7 22.5% 99.6% 75.2% 90.4% 2 91.0% 140.5% 115.7% 115.7% ~ ~ ~ 14 22.5% 140.5% 89.5% 96.2% E-9 ------- Table E-l. Evaluation of Accuracy - Relative Percent Difference versus Reference Laboratory Data Calculated for the Xcalibur ElvaX (Continued) Matrix Soil Cone Range Level 1 Level 2 Level 3 Level 4 All Soil Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Nickel 24 1.5% 35.4% 17.7% 16.7% 5 6.1% 39.1% 28.2% 30.9% 6 3.7% 25.4% 15.4% 13.6% ~ 35 1.5% 39.1% 18.8% 17.0% Selenium 2 0.9% 3.7% 2.3% 2.3% 5 51.2% 86.3% 72.5% 72.7% 4 75.7% 106.0% 89.6% 88.3% ~ 11 0.9% 106.0% 66.0% 75.7% Silver 3 2.6% 16.2% 10.1% 11.6% 3 0.0% 15.4% 7.7% 7.6% 7 3.6% 106.7% 35.1% 16.5% ~ 13 0.0% 106.7% 23.0% 12.4% Vanadium 3 13.2% 50.4% 33.0% 35.4% 3 47.6% 77.4% 65.2% 70.6% 4 64.2% 129.5% 87.7% 78.6% ~ 10 13.2% 129.5% 64.6% 67.4% Zinc 20 0.1% 80.6% 30.9% 21.6% 6 0.8% 52.2% 31.5% 35.2% 9 0.3% 105.7% 26.6% 22.2% ~ 35 0.1% 105.7% 29.9% 22.3% E-10 ------- Table E-l. Evaluation of Accuracy - Relative Percent Difference versus Reference Laboratory Data Calculated for the Xcalibur ElvaX (Continued) Matrix Sediment Cone Range Level 1 Level 2 Level 3 Level 4 All Sediment Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Antimony RefLab ERA Spike 3 3 30.6% 4.1% 45.5% 100.0% 39.9% 38.5% 43.8% 11.5% 4 4 27.0% 2.6% 55.7% 18.8% 39.9% 9.9% 38.4% 9.2% 3 3 59.9% 0.1% 63.0% 4.2% 61.7% 2.3% 62.3% 2.7% 10 10 27.0% 0.1% 63.0% 100.0% 46.4% 16.2% 45.6% 6.2% Arsenic 17 1.9% 104.0% 55.9% 42.5% 4 2.2% 52.7% 28.7% 29.9% 2 41.1% 57.3% 49.2% 49.2% ~ 23 1.9% 104.0% 50.6% 42.5% Cadmium 3 11.8% 44.3% 23.4% 14.0% 4 22.5% 37.1% 29.7% 29.6% 3 5.6% 21.0% 14.8% 17.7% ~ 10 5.6% 44.3% 23.3% 21.7% Chromium 6 4.8% 30.7% 19.4% 20.6% 3 34.0% 35.9% 34.8% 34.6% 3 36.2% 46.8% 40.2% 37.8% ~ 12 4.8% 46.8% 28.5% 32.4% Copper 8 4.6% 101.8% 43.0% 33.0% 4 1.2% 8.3% 4.8% 4.8% 10 7.3% 48.7% 26.7% 27.2% ~ 22 1.2% 101.8% 28.7% 25.1% Iron o 3 10.9% 73.9% 34.7% 19.2% 19 1.2% 34.7% 15.0% 14.0% 4 16.2% 30.9% 23.3% 23.0% 6 12.4% 44.8% 28.5% 30.6% 32 1.2% 73.9% 20.4% 17.6% Lead 12 5.7% 121.2% 67.0% 68.1% o 3 42.5% 66.4% 56.2% 59.9% o 3 51.0% 88.7% 73.7% 81.2% ~ 18 5.7% 121.2% 66.3% 66.9% Mercury 3 80.5% 103.7% 91.3% 89.8% 4 70.9% 106.7% 84.0% 79.2% 3 72.3% 92.4% 84.4% 88.5% ~ 10 70.9% 106.7% 86.3% 84.5% E-ll ------- Table E-l. Evaluation of Accuracy - Relative Percent Difference versus Reference Laboratory Data Calculated for the Xcalibur ElvaX (Continued) Matrix Sediment Cone Range Level 1 Level 2 Level 3 Level 4 All Sediment Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Nickel 18 3.6% 73.9% 26.3% 22.1% 6 2.9% 22.8% 15.3% 17.4% 4 1.2% 36.0% 18.5% 18.5% ~ ~ ~ 28 1.2% 73.9% 22.8% 20.0% Selenium 3 6.5% 59.5% 28.7% 20.0% 4 42.6% 110.0% 72.0% 67.7% 3 91.7% 98.5% 95.9% 97.4% ~ ~ ~ 10 6.5% 110.0% 66.2% 69.1% Silver 4 16.1% 57.1% 42.6% 48.6% 4 15.5% 51.1% 31.9% 30.4% o 5 50.3% 93.9% 70.8% 68.3% ~ ~ ~ 11 15.5% 93.9% 46.4% 50.3% Vanadium 0 NC NC NC NC o 3 55.1% 87.0% 72.1% 74.2% o 5 75.8% 93.1% 84.1% 83.3% ~ ~ ~ 6 55.1% 93.1% 78.1% 79.5% Zinc 17 2.1% 70.9% 34.6% 33.9% 5 34.9% 63.4% 47.8% 50.8% 4 18.6% 60.1% 35.0% 30.6% ~ ~ ~ 26 2.1% 70.9% 37.2% 37.2% E-12 ------- Table E-l. Evaluation of Accuracy - Relative Percent Difference versus Reference Laboratory Data Calculated for the Xcalibur ElvaX (Continued) Matrix All Samples All Samples Cone Range Xcalibur ElvaX All Instruments Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Antimony RefLab 27 2.6% 105.4% 44.9% 45.5% 206 0.1% 181.5% 80.6% 84.3% ERA Spike 14 0.1% 154.4% 23.6% 6.2% 110 0.1% 162.0% 62.7% 70.6% Arsenic 46 1.9% 163.0% 49.1% 44.2% 320 0.2% 182.8% 36.6% 26.2% Cadmium 26 0.2% 44.3% 18.3% 16.3% 209 0.1% 168.1% 29.6% 16.7% Chromium 41 2.3% 87.2% 30.6% 30.7% 338 0.1% 151.7% 30.8% 26.0% Copper 48 1.2% 111.1% 37.3% 25.1% 363 0.2% 111.1% 24.6% 16.2% Iron 70 0.3% 73.9% 21.1% 19.5% 558 0.0% 190.1% 35.4% 26.0% Lead 42 0.5% 121.2% 54.0% 54.6% 392 0.1% 135.2% 30.9% 21.5% Mercury 24 22.5% 140.5% 88.2% 90.7% 192 0.0% 158.1% 62.5% 58.6% Table E-l. Evaluation of Accuracy - Relative Percent Difference versus Reference Laboratory Data Calculated for the Xcalibur ElvaX (Continued) Matrix All Samples All Samples Cone Range Xcalibur ElvaX All Instruments Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Nickel 63 1.2% 73.9% 20.6% 17.5% 403 0.3% 146.5% 31.0% 25.4% Selenium 21 0.9% 110.0% 66.1% 75.7% 195 0.0% 127.1% 32.0% 16.7% Silver 24 0.0% 106.7% 33.7% 18.3% 177 0.0% 129.7% 36.0% 28.7% Vanadium 16 13.2% 129.5% 69.6% 74.0% 218 0.1% 129.5% 42.2% 38.3% Zinc 61 0.1% 105.7% 33.0% 32.5% 471 0.0% 138.0% 26.3% 19.4% E-13 ------- Table E-l. Evaluation of Accuracy - Relative Percent Difference versus Reference Laboratory Data Calculated for the Xcalibur ElvaX (Continued) Notes: All RPDs presented in this table are absolute values. No samples reported by the reference laboratory in this concentration range. Cone Concentration. ERA Environmental Resource Associates, Inc. NC Not calculated because of a lack of XRF data. Number Number of demonstration samples evaluated. Ref Lab Reference laboratory (Shealy Environmental Services, Inc.). RPD Relative percent difference. XRF X-ray fluorescence. E-14 ------- Table E-2. Evaluation of Precision - Relative Standard Deviations Calculated for the Xcalibur ElvaX Matrix Soil Cone Range Low Medium High Very High All Soil Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Antimony 9 3.0% 24.2% 10.7% 6.7% 5 1.6% 11.0% 5.3% 3.0% 3 1.8% 19.0% 8.1% 3.6% ~ ~ 17 1.6% 24.2% 8.6% 6.5% Arsenic 15 6.4% 51.3% 21.4% 16.1% 4 5.9% 34.7% 14.0% 7.7% 4 3.5% 21.8% 14.3% 16.0% ~ ~ 23 3.5% 51.3% 18.9% 14.8% Cadmium 7 4.7% 35.2% 20.8% 20.5% 7 1.8% 9.4% 4.1% 2.2% 2 4.5% 4.5% 4.5% 4.5% ~ ~ 16 1.8% 35.2% 11.4% 6.3% Chromium 23 6.5% 48.5% 23.4% 20.9% 4 2.5% 14.1% 6.9% 5.5% 2 1.7% 3.2% 2.4% 2.4% ~ - 29 1.7% 48.5% 19.7% 17.7% Copper 16 2.0% 20.5% 7.4% 6.2% 8 1.2% 11.3% 5.2% 3.8% 2 6.0% 19.5% 12.8% 12.8% ~ ~ 26 1.2% 20.5% 7.1% 6.0% Iron 5 1.8% 7.7% 4.8% 4.4% 13 0.7% 11.7% 3.5% 2.7% 13 1.5% 15.5% 5.5% 3.8% 7 2.8% 12.2% 5.7% 4.5% 38 0.7% 15.5% 4.8% 4.1% Lead 7 1.9% 25.2% 9.3% 7.0% 4 3.5% 23.9% 9.0% 4.2% 8 0.7% 19.3% 5.0% 2.6% 5 1.1% 15.8% 8.7% 10.4% 24 0.7% 25.2% 7.7% 4.6% Mercury 5 26.2% 137.1% 54.3% 37.7% 7 7.1% 18.1% 13.3% 12.6% 2 4.6% 8.0% 6.3% 6.3% ~ ~ 14 4.6% 137.1% 26.9% 15.7% E-15 ------- Table E-2. Evaluation of Precision - Relative Standard Deviations Calculated for the Xcalibur ElvaX (Continued) Matrix Soil Cone Range Low Medium High Very High All Soil Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Nickel 24 2.9% 37.7% 14.3% 10.3% 5 2.6% 17.7% 8.1% 6.3% 6 1.6% 6.8% 3.5% 2.6% ~ ~ ~ ~ 35 1.6% 37.7% 11.6% 7.9% Selenium 2 18.9% 35.1% 27.0% 27.0% 5 2.0% 13.6% 6.5% 5.2% 4 5.8% 9.1% 7.9% 8.3% ~ ~ ~ ~ 11 2.0% 35.1% 10.7% 8.5% Silver 3 8.6% 21.4% 13.8% 11.5% 3 7.2% 10.9% 8.5% 7.3% 7 7.9% 23.8% 16.8% 19.2% ~ ~ ~ ~ 13 7.2% 23.8% 14.2% 11.5% Vanadium 3 43.4% 52.3% 48.4% 49.4% 3 7.7% 40.8% 23.9% 23.3% 4 13.5% 42.0% 28.3% 28.9% ~ ~ ~ ~ 10 7.7% 52.3% 33.0% 39.9% Zinc 20 1.8% 24.4% 9.4% 8.1% 6 0.4% 7.3% 3.2% 2.3% 9 0.3% 10.8% 4.0% 1.8% ~ ~ ~ ~ 35 0.3% 24.4% 7.0% 6.4% E-16 ------- Table E-2. Evaluation of Precision - Relative Standard Deviations Calculated for the Xcalibur ElvaX (Continued) Matrix Sediment Cone Range Low Medium High Very High All Sediment Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Antimony 3 3.8% 9.0% 6.0% 5.1% 4 3.5% 10.7% 6.7% 6.3% 3 1.6% 13.2% 6.1% 3.4% ~ ~ 10 1.6% 13.2% 6.3% 5.2% Arsenic 17 6.3% 41.3% 19.2% 18.5% 4 3.7% 7.2% 5.0% 4.6% 2 1.4% 2.9% 2.2% 2.2% ~ ~ 23 1.4% 41.3% 15.2% 14.1% Cadmium 3 7.4% 16.0% 10.5% 8.1% 4 3.6% 7.0% 5.4% 5.5% 3 2.3% 7.9% 4.5% 3.2% ~ ~ 10 2.3% 16.0% 6.6% 6.5% Chromium 6 9.0% 37.2% 27.0% 30.0% 3 4.7% 16.0% 8.7% 5.4% 3 3.7% 5.7% 4.8% 5.0% ~ ~ 12 3.7% 37.2% 16.9% 12.5% Copper 8 2.3% 18.1% 7.8% 6.1% 4 1.9% 3.3% 2.4% 2.3% 10 2.3% 13.1% 5.6% 4.3% ~ ~ 22 1.9% 18.1% 5.8% 4.3% Iron 3 3.4% 9.8% 6.0% 4.9% 19 0.4% 8.2% 2.5% 2.2% 4 0.9% 9.8% 3.9% 2.4% 6 1.4% 6.2% 3.3% 3.2% 32 0.4% 9.8% 3.1% 2.5% Lead 12 2.9% 47.0% 16.2% 12.5% 3 1.3% 3.9% 2.8% 3.2% 3 2.2% 6.5% 3.8% 2.7% ~ ~ 18 1.3% 47.0% 11.9% 6.4% Mercury 3 35.5% 44.0% 40.8% 42.8% 4 1.9% 12.1% 6.5% 5.9% 3 3.0% 5.2% 4.5% 5.2% ~ ~ 10 1.9% 44.0% 16.1% 6.5% E-17 ------- Table E-2. Evaluation of Precision - Relative Standard Deviations Calculated for the Xcalibur ElvaX (Continued) Matrix Sediment Cone Range Low Medium High Very High All Sediment Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Nickel 18 0.9% 35.4% 11.1% 9.9% 6 4.0% 10.5% 6.4% 5.9% 4 1.1% 8.7% 3.4% 1.8% ~ ~ ~ ~ 28 0.9% 35.4% 9.0% 8.2% Selenium 3 16.0% 48.6% 27.3% 17.3% 4 2.3% 11.4% 8.2% 9.6% 3 2.8% 6.1% 4.2% 3.6% ~ ~ ~ ~ 10 2.3% 48.6% 12.7% 9.6% Silver 4 2.2% 13.6% 8.6% 9.4% 4 3.4% 15.5% 7.5% 5.6% 3 2.0% 13.8% 6.3% 3.2% ~ ~ ~ ~ 11 2.0% 15.5% 7.6% 7.0% Vanadium 0 NC NC NC NC 3 7.2% 30.0% 21.0% 25.7% 3 4.4% 16.9% 9.0% 5.6% ~ ~ ~ ~ 6 4.4% 30.0% 15.0% 12.1% Zinc 17 1.2% 31.5% 10.2% 8.3% 5 1.1% 5.2% 3.2% 3.3% 4 1.3% 2.1% 1.7% 1.8% ~ ~ ~ ~ 26 1.1% 31.5% 7.6% 5.8% E-18 ------- Table E-2. Evaluation of Precision - Relative Standard Deviations Calculated for the Xcalibur ElvaX (Continued) Matrix All Samples All Samples Cone Range Xcalibur ElvaX All Instruments Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Antimony 27 1.6% 24.2% 7.8% 5.4% 206 0.5% 97.7% 8.9% 6.1% Arsenic 46 1.4% 51.3% 17.1% 14.1% 320 0.2% 71.7% 11.2% 8.2% Cadmium 26 1.8% 35.2% 9.6% 6.5% 209 0.4% 92.8% 8.2% 3.6% Chromium 41 1.7% 48.5% 18.9% 17.2% 338 0.6% 116.3% 15.9% 12.1% Copper 48 1.2% 20.5% 6.5% 4.9% 363 0.1% 58.3% 7.5% 5.1% Iron 70 0.4% 15.5% 4.0% 3.2% 558 0.1% 101.8% 5.2% 2.2% Lead 42 0.7% 47.0% 9.5% 6.0% 392 0.2% 115.6% 9.3% 4.9% Mercury 24 1.9% 137.1% 22.4% 12.5% 192 1.0% 137.1% 14.3% 6.8% Table E-2. Evaluation of Precision - Relative Standard Deviations Calculated for the Xcalibur ElvaX (Continued) Matrix All Samples All Samples Cone Range Xcalibur ElvaX All Instruments Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Nickel 63 0.9% 37.7% 10.4% 8.0% 403 0.3% 164.2% 10.8% 7.0% Selenium 21 2.0% 48.6% 11.7% 8.9% 195 0.1% 98.8% 7.2% 4.5% Silver 24 2.0% 23.8% 11.2% 9.4% 177 0.6% 125.3% 10.3% 5.2% Vanadium 16 4.4% 52.3% 26.2% 24.5% 218 0.4% 86.1% 12.5% 8.5% Zinc 61 0.3% 31.5% 7.2% 6.1% 471 0.1% 192.9% 8.0% 5.3% Notes: Cone NC Number RSD XRF No samples reported by the reference laboratory in this concentration range. Concentration. Not calculated because of a lack of XRF data. Number of demonstration samples evaluated. Relative standard deviation. X-ray fluorescence. E-19 ------- Table E-3. Evaluation of Precision - Relative Standard Deviations Calculated for the Reference Laboratory Matrix All Soil All Sediment All Samples Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Antimony 17 3.6% 38.0% 14.3% 9.8% 7 2.9% 33.6% 14.4% 9.1% 24 2.9% 38.0% 14.3% 9.5% Arsenic 23 1.4% 45.8% 11.7% 12.4% 24 2.4% 36.7% 10.7% 9.2% 47 1.4% 45.8% 11.2% 9.5% Cadmium 15 0.9% 21.4% 11.1% 9.0% 10 2.9% 37.5% 11.4% 8.2% 25 0.9% 37.5% 11.2% 9.0% Chromium 34 1.4% 137.0% 14.3% 10.6% 26 4.6% 35.5% 9.8% 7.5% 60 1.4% 137.0% 12.4% 8.4% Copper 26 0.0% 21.0% 10.1% 9.1% 21 1.8% 38.8% 9.7% 8.9% 47 0.0% 38.8% 9.9% 8.9% Iron 38 1.6% 46.2% 10.2% 8.7% 31 2.7% 37.5% 9.9% 8.1% 69 1.6% 46.2% 10.1% 8.5% Lead 33 0.0% 150.0% 17.6% 13.2% 22 0.0% 41.1% 11.6% 7.4% 55 0.0% 150.0% 15.2% 8.6% Mercury 16 0.0% 50.7% 13.8% 6.6% 10 2.8% 48.0% 14.3% 6.9% 26 0.0% 50.7% 14.0% 6.6% Table E-3. Evaluation of Precision - Relative Standard Deviations Calculated for the Reference Laboratory (Continued) Matrix All Soil All Sediment All Samples Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Nickel 35 0.0% 44.9% 11.4% 10.0% 27 0.6% 35.8% 9.4% 7.3% 62 0.0% 44.9% 10.6% 8.2% Selenium 13 0.0% 22.7% 8.9% 7.1% 12 1.3% 37.3% 10.0% 7.6% 25 0.0% 37.3% 9.4% 7.4% Silver 13 2.3% 37.1% 12.4% 7.5% 10 1.0% 21.3% 9.4% 6.6% 23 1.0% 37.1% 11.1% 7.1% Vanadium 21 0.0% 18.1% 8.4% 6.6% 17 2.2% 21.9% 8.4% 8.1% 38 0.0% 21.9% 8.4% 7.2% Zinc 35 1.0% 46.5% 10.4% 9.1% 27 1.4% 35.8% 8.9% 6.9% 62 1.0% 46.5% 9.8% 7.4% E-20 ------- Table E-4. Evaluation of the Effects of Interferent Elements on RPDs (Accuracy) of Other Target Elements1 Parameter Interferent/Element Ratio Number of Samples RPD of Target Element2 RPD of Target Element (Absolute Value)2 Interferent Concentration Range Target Element Concentration Range Statistic Minimum Maximum Mean Median Minimum Maximum Mean Median Minimum Maximum Mean Median Minimum Maximum Mean Median Lead Effects on Arsenic <5 29 -163.0% 8.1% -55.0% -45.1% 2.2% 163.0% 55.5% 45.1% ND 1314 299 152 67 4480 452 178 5-10 7 -33.7% 22.2% -11.7% -9.7% 8.4% 33.7% 18.0% 21.5% 1163 54373 19071 8802 163 6033 2068 1129 >10 10 -104.0% 53.8% -22.9% -31.9% 1.9% 104.0% 52.2% 50.6% 2326 38476 8482 4699 59 2434 310 70 Copper Effects on Nickel <5 44 -24.1% 39.1% 14.0% 16.7% 1.2% 39.1% 18.4% 17.2% ND 1085 193 73 48 2644 476 146 5-10 5 -3.6% 33.9% 12.1% 15.7% 2.9% 33.9% 14.7% 15.7% 852 2137 1372 1143 78 244 152 131 >10 14 -73.9% 27.7% -17.3% -21.7% 4.0% 73.9% 29.6% 27.6% 682 9436 3473 2298 58 629 172 122 Nickel Effects on Copper <5 39 -108.7% 53.0% -22.2% -11.2% 1.2% 108.7% 31.4% 21.0% ND 629 163 128 29 9436 1669 852 5-10 1 70.7% 70.7% 70.7% 70.7% 70.7% 70.7% 70.7% 70.7% 307 307 307 307 37 37 37 37 >10 8 -111.1% 32.4% -40.3% -44.9% 22.8% 111.1% 61.7% 49.4% 1070 2644 1888 1793 60 438 213 122 E-21 ------- Table E-4. Evaluation of the Effects of Interferent Elements on RPDs (Accuracy) of Other Target Elements1 (Continued) Parameter Interferent/Element Ratio Number of Samples RPD of Target Element2 RPD of Target Element (Absolute Value)2 Interferent Concentration Range Target Element Concentration Range Statistic Minimum Maximum Mean Median Minimum Maximum Mean Median Minimum Maximum Mean Median Minimum Maximum Mean Median Zinc Effects on Copper <5 35 -64.4% 70.7% -4.2% -7.3% 1.2% 70.7% 23.0% 21.0% ND 7370 1267 177 29 9436 1760 909 5-10 2 -9.9% 6.1% -1.9% -1.9% 6.1% 9.9% 8.0% 8.0% 1085 9253 5169 5169 177 1374 775 775 >10 11 -111.1% -23.3% -87.9% -99.1% 23.3% 111.1% 87.9% 99.1% 1384 5331 3447 3528 104 639 336 332 Copper Effects on Zinc <5 49 -80.6% 105.7% -24.4% -25.3% 0.1% 105.7% 32.0% 32.5% ND 2205 386 177 36 9253 1944 1085 5-10 3 -47.1% 70.9% 13.8% 17.6% 17.6% 70.9% 45.2% 47.1% 634 2187 1302 1085 95 165 120 99 >10 9 -65.0% 56.2% -0.4% 2.3% 2.3% 65.0% 34.7% 31.3% 1818 9436 4692 3670 92 562 183 103 Notes: 1. Concentrations are reported in units of milligrams per kilogram (mg/kg), or parts per million (ppm). 2. Table presents statistics for raw (unmodified) RPDs as well as absolute value RPDs. < Less than. > Greater than. RPD Relative percent difference. NC Not calculated because of a lack of XRF data. ND Nondetect. XRF X-ray fluorescence. E-22 ------- Table E-5. Evaluation of the Effects of Soil Type on RPDs (Accuracy) of Target Elements Matrix Soil Soil Soil Soil& Sediment Site AS BN CN KP Matrix Description Fine to medium sand (steel processing) Sandy loam, low organic (ore residuals) Sandy loam (burn pit residue) Soil: Fine to medium quartz sand. Sed. : Sandy loam, high organic. (Gun and skeet ranges.) Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Antimony Reference Laboratory RPD ~ ~ ~ 4 -2.7% 71.9% 23.6% 12.6% 2 67.6% 70.2% 68.9% 68.9% 1 48.2% 48.2% 48.2% 48.2% RPD ABS Val ~ ~ ~ 4 2.7% 71.9% 24.9% 12.6% 2 67.6% 70.2% 68.9% 68.9% 1 48.2% 48.2% 48.2% 48.2% Certified Value RPD ~ ~ ~ 1 6.3% 6.3% 6.3% 6.3% 2 6.2% 154.4% 80.3% 80.3% - RPD ABS Val ~ ~ ~ 1 6.3% 6.3% 6.3% 6.3% 2 6.2% 154.4% 80.3% 80.3% - Arsenic Reference Laboratory RPD 1 -82.6% -82.6% -82.6% -82.6% 7 -63.7% 43.3% -19.9% -22.1% 1 -66.2% -66.2% -66.2% -66.2% ~ RPD ABS Val 1 82.6% 82.6% 82.6% 82.6% 7 8.4% 63.7% 32.3% 33.7% 1 66.2% 66.2% 66.2% 66.2% ~ Cadmium Reference Laboratory RPD 3 -13.1% 25.0% 4.0% 0.2% 5 -21.6% 5.3% -9.8% -10.1% 2 -23.0% -0.4% -11.7% -11.7% ~ RPD ABS Val 3 0.2% 25.0% 12.8% 13.1% 5 5.3% 21.6% 11.9% 10.1% 2 0.4% 23.0% 11.7% 11.7% ~ E-23 ------- Table E-5. Evaluation of the Effects of Soil Type on RPDs (Accuracy) of Target Elements (Continued) Matrix Soil Soil Soil Soil& Sediment Site AS BN CN KP Matrix Description Fine to medium sand (steel processing) Sandy loam, low organic (ore residuals) Sandy loam (burn pit residue) Soil: Fine to medium quartz sand. Sed. : Sandy loam, high organic. (Gun and skeet ranges.) Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Chromium Reference Laboratory RPD 2 6.1% 11.6% 8.8% 8.8% 5 31.6% 58.1% 42.1% 43.2% 1 21.2% 21.2% 21.2% 21.2% 4 -20.1% 8.9% -5.5% -5.4% RPDABS Val 2 6.1% 11.6% 8.8% 8.8% 5 31.6% 58.1% 42.1% 43.2% 1 21.2% 21.2% 21.2% 21.2% 4 4.8% 20.1% 10.0% 7.5% Copper Reference Laboratory RPD 3 -86.3% -59.7% -76.5% -83.7% 6 -111.1% 30.4% -17.3% -6.6% 3 -72.5% 1.3% -30.7% -21.0% 2 15.7% 22.8% 19.2% 19.2% RPDABS Val 3 59.7% 86.3% 76.5% 83.7% 6 2.0% 111.1% 28.5% 12.1% 3 1.3% 72.5% 31.6% 21.0% 2 15.7% 22.8% 19.2% 19.2% Iron Reference Laboratory RPD 3 1.3% 31.2% 17.4% 19.7% 7 -10.3% 33.9% 11.3% 5.7% 3 -2.8% 19.8% 6.3% 1.9% 6 -19.2% 46.2% 8.2% 3.9% RPDABS Val 3 1.3% 31.2% 17.4% 19.7% 7 1.1% 33.9% 14.8% 10.3% 3 1.9% 19.8% 8.2% 2.8% 6 0.3% 46.2% 18.3% 15.1% Lead Reference Laboratory RPD 3 -67.0% -40.2% -51.8% -48.1% 6 -50.5% 10.9% -31.7% -43.8% 2 -71.2% -32.2% -51.7% -51.7% 6 -43.0% 8.3% -5.6% 0.8% RPDABS Val 3 40.2% 67.0% 51.8% 48.1% 6 10.9% 50.5% 35.3% 43.8% 2 32.2% 71.2% 51.7% 51.7% 6 0.5% 43.0% 10.8% 5.3% E-24 ------- Table E-5. Evaluation of the Effects of Soil Type on RPDs (Accuracy) of Target Elements (Continued) Matrix Soil Soil Soil Soil& Sediment Site AS BN CN KP Matrix Description Fine to medium sand (steel processing) Sandy loam, low organic (ore residuals) Sandy loam (burn pit residue) Soil: Fine to medium quartz sand. Sed. : Sandy loam, high organic. (Gun and skeet ranges.) Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Mercury Reference Laboratory RPD ~ ~ ~ 1 -26.6% -26.6% -26.6% -26.6% 2 90.4% 107.9% 99.2% 99.2% ~ RPDABS Val ~ ~ ~ 1 26.6% 26.6% 26.6% 26.6% 2 90.4% 107.9% 99.2% 99.2% ~ Nickel Reference Laboratory RPD 3 -39.1% 25.8% -1.3% 9.3% 6 -9.8% 27.7% 16.5% 20.1% 3 -14.8% 30.9% 14.6% 27.6% 3 -9.8% 12.0% 0.2% -1.5% RPDABS Val 3 9.3% 39.1% 24.7% 25.8% 6 9.8% 27.7% 19.8% 20.1% 3 14.8% 30.9% 24.4% 27.6% 3 1.5% 12.0% 7.8% 9.8% Selenium Reference Laboratory RPD 1 -68.5% -68.5% -68.5% -68.5% 2 -75.7% -51.2% -63.4% -63.4% 2 -72.7% 0.9% -35.9% -35.9% ~ RPD ABS Val 1 68.5% 68.5% 68.5% 68.5% 2 51.2% 75.7% 63.4% 63.4% 2 0.9% 72.7% 36.8% 36.8% - Silver Reference Laboratory RPD 1 -16.5% -16.5% -16.5% -16.5% 4 -106.7% 0.0% -29.2% -5.1% 2 -15.4% -11.6% -13.5% -13.5% ~ RPD ABS Val 1 16.5% 16.5% 16.5% 16.5% 4 0.0% 106.7% 29.2% 5.1% 2 11.6% 15.4% 13.5% 13.5% ~ E-25 ------- Table E-5. Evaluation of the Effects of Soil Type on RPDs (Accuracy) of Target Elements (Continued) Matrix Soil Soil Soil Soil& Sediment Site AS BN CN KP Matrix Description Fine to medium sand (steel processing) Sandy loam, low organic (ore residuals) Sandy loam (burn pit residue) Soil: Fine to medium quartz sand. Sed. : Sandy loam, high organic. (Gun and skeet ranges.) Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Vanadium Reference Laboratory RPD ~ ~ ~ ~ 2 77.4% 129.5% 103.4% 103.4% 1 70.6% 70.6% 70.6% 70.6% - RPDABS Val ~ ~ ~ ~ 2 77.4% 129.5% 103.4% 103.4% 1 70.6% 70.6% 70.6% 70.6% - Zinc Reference Laboratory RPD 3 -65.0% 105.7% 13.8% 0.8% 7 -61.6% -8.3% -36.8% -33.4% 3 -80.6% -15.2% -49.4% -52.2% 2 -57.3% -47.1% -52.2% -52.2% RPDABS Val 3 0.8% 105.7% 57.1% 65.0% 7 8.3% 61.6% 36.8% 33.4% 3 15.2% 80.6% 49.4% 52.2% 2 47.1% 57.3% 52.2% 52.2% E-26 ------- Table E-5. Evaluation of the Effects of Soil Type on RPDs (Accuracy) of Target Elements (Continued) Matrix Sediment Sediment Soil Sediment Soil Site LV RF SB TL WS All Matrix Description Clay /clay loam, salt crust (iron and other precipitate) Silty fine sand (tailings) Coarse sand and gravel (ore and waste rock) Silt and clay (slag- enriched) Coarse sand and gravel (roaster slag) Samples Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Antimony Reference Laboratory RPD 4 35.9% 49.6% 42.2% 41.6% 4 -43.8% 63.0% 34.3% 59.0% 6 -68.5% 43.9% 9.7% 23.0% 3 -45.7% -27.0% -39.4% -45.5% 3 -105.4% -37.6% -63.3% -47.0% 27 -105.4% 77.4% 11.3% 14.9% RPDABS Val 4 35.9% 49.6% 42.2% 41.6% 4 43.8% 63.0% 56.2% 59.0% 6 2.6% 68.5% 32.5% 32.9% 3 27.0% 45.7% 39.4% 45.5% 3 37.6% 105.4% 63.3% 47.0% 27 2.6% 105.4% 44.9% 45.5% Certified Value RPD 4 -108.4% 32.4% -15.1% 7.8% 4 -2.6% 98.9% 24.8% 1.4% ~ ~ ~ ~ 3 10.2% 18.8% 13.5% 11.5% ~ ~ ~ 14 -2.6% 154.4% 23.0% 6.2% RPDABS Val 4 9.9% 108.4% 44.0% 28.9% 4 0.1% 98.9% 26.1% 2.7% ~ ~ ~ ~ o 3 10.2% 18.8% 13.5% 11.5% ~ ~ ~ 14 0.1% 154.4% 23.5% 6.2% Arsenic Reference Laboratory RPD 12 -31.8% 73.9% 16.5% 17.3% 12 -88.4% -25.7% -44.8% -41.8% 5 -163.0% -39.2% -76.5% -48.6% 2 -70.4% 1.9% -34.3% -34.3% 7 -66.4% 47.4% -14.3% -18.6% 46 -163.0% 53.8% -41.4% -41.0% RPDABS Val 12 1.2% 73.9% 27.5% 28.4% 12 25.7% 88.4% 44.8% 41.8% 5 39.2% 163.0% 76.5% 48.6% 2 1.9% 70.4% 36.2% 36.2% 7 8.4% 66.4% 34.2% 22.2% 46 1.9% 163.0% 49.1% 44.2% Cadmium Reference Laboratory RPD 4 -97.3% -59.2% -81.2% -84.2% 5 -37.1% -11.8% -22.0% -21.0% 1 -16.3% -16.3% -16.3% -16.3% 2 -34.3% -14.0% -24.1% -24.1% o 5 -29.4% -12.2% -18.7% -14.7% 26 -44.3% 25.0% -15.9% -15.5% RPD ABS Val 4 59.2% 97.3% 81.2% 84.2% 5 11.8% 37.1% 22.0% 21.0% 1 16.3% 16.3% 16.3% 16.3% 2 14.0% 34.3% 24.1% 24.1% o 5 12.2% 29.4% 18.7% 14.7% 26 0.2% 44.3% 18.3% 16.3% E-27 ------- Table E-5. Evaluation of the Effects of Soil Type on RPDs (Accuracy) of Target Elements (Continued) Matrix Sediment Sediment Soil Sediment Soil Site LV RF SB TL WS All Matrix Description Clay /clay loam, salt crust (iron and other precipitate) Silty fine sand (tailings) Coarse sand and gravel (ore and waste rock) Silt and clay (slag- enriched) Coarse sand and gravel (roaster slag) Samples Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Chromium Reference Laboratory RPD 3 70.9% 121.0% 93.5% 88.5% 8 11.7% 37.8% 29.8% 32.4% 10 -34.8% 87.2% 21.8% 19.5% 1 15.6% 15.6% 15.6% 15.6% 6 -41.9% 80.4% 28.5% 30.1% 41 -41.9% 87.2% 25.3% 28.1% RPDABS Val 3 70.9% 121.0% 93.5% 88.5% 8 11.7% 37.8% 29.8% 32.4% 10 9.0% 87.2% 28.8% 22.9% 1 15.6% 15.6% 15.6% 15.6% 6 2.3% 80.4% 42.4% 38.7% 41 2.3% 87.2% 30.6% 30.7% Copper Reference Laboratory RPD 11 -24.1% 39.1% 8.9% 11.5% 13 -101.8% 70.7% -11.0% -8.3% 4 -108.7% 53.0% -33.0% -38.1% 7 -48.7% -18.2% -32.1% -28.6% 6 -105.3% 9.2% -28.3% -7.6% 48 -111.1% 70.7% -23.3% -11.4% RPDABS Val 11 3.7% 39.1% 18.7% 14.3% 13 1.2% 101.8% 28.5% 11.6% 4 22.8% 108.7% 70.9% 76.1% 7 18.2% 48.7% 32.1% 28.6% 6 5.4% 105.3% 33.4% 9.5% 48 1.2% 111.1% 37.3% 25.1% Iron Reference Laboratory RPD 5 -97.4% 6.5% -68.8% -84.1% 13 -5.3% 28.8% 13.9% 16.2% 12 3.2% 44.0% 29.7% 33.7% 7 -34.7% 15.7% -9.0% -1.9% 7 -16.4% 32.4% 19.3% 23.8% 70 -34.7% 73.9% 14.4% 17.6% RPDABS Val 5 6.5% 97.4% 71.3% 84.1% 13 5.0% 28.8% 15.5% 16.2% 12 3.2% 44.0% 29.7% 33.7% 7 1.9% 34.7% 18.2% 15.7% 7 16.4% 32.4% 24.0% 23.8% 70 0.3% 73.9% 21.1% 19.5% Lead Reference Laboratory RPD 4 -68.3% 3.6% -27.4% -22.4% 10 -76.3% -42.5% -58.6% -59.0% ~ ~ ~ ~ 4 -121.2% -66.4% -95.1% -96.4% 7 -88.5% -22.3% -63.3% -70.5% 42 -121.2% 10.9% -52.8% -54.6% RPD ABS Val 4 3.6% 68.3% 29.1% 22.4% 10 42.5% 76.3% 58.6% 59.0% ~ ~ ~ ~ 4 66.4% 121.2% 95.1% 96.4% 7 22.3% 88.5% 63.3% 70.5% 42 0.5% 121.2% 54.0% 54.6% E-28 ------- Table E-5. Evaluation of the Effects of Soil Type on RPDs (Accuracy) of Target Elements (Continued) Matrix Sediment Sediment Soil Sediment Soil Site LV RF SB TL WS All Matrix Description Clay /clay loam, salt crust (iron and other precipitate) Silty fine sand (tailings) Coarse sand and gravel (ore and waste rock) Silt and clay (slag- enriched) Coarse sand and gravel (roaster slag) Samples Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Mercury Reference Laboratory RPD 3 70.9% 121.0% 93.5% 88.5% 5 79.3% 106.7% 89.7% 89.8% 10 -133.5% 140.5% 64.0% 92.4% o 5 72.3% 103.7% 85.0% 79.1% ~ ~ ~ 24 -133.5% 140.5% 74.8% 90.1% RPDABS Val 3 70.9% 121.0% 93.5% 88.5% 5 79.3% 106.7% 89.7% 89.8% 10 22.5% 140.5% 90.7% 96.2% o 5 72.3% 103.7% 85.0% 79.1% ~ ~ ~ 24 22.5% 140.5% 88.2% 90.7% Nickel Reference Laboratory RPD 11 -24.1% 39.1% 8.9% 11.5% 13 -2.9% 34.5% 17.7% 19.9% 11 -7.5% 35.4% 19.0% 17.5% 6 -73.9% -3.6% -35.5% -36.4% 7 -37.3% 23.2% -4.4% 4.0% 63 -73.9% 39.1% 6.9% 13.6% RPDABS Val 11 3.7% 39.1% 18.7% 14.3% 13 1.2% 34.5% 18.1% 19.9% 11 7.5% 35.4% 20.4% 17.5% 6 3.6% 73.9% 35.5% 36.4% 7 4.0% 37.3% 18.6% 16.3% 63 1.2% 73.9% 20.6% 17.5% Selenium Reference Laboratory RPDABS RPD Val 5 5 -97.4% 6.5% 6.5% 97.4% -68.8% 71.3% -84.1% 84.1% 3 3 -98.5% 56.8% -56.8% 98.5% -82.3% 82.3% -91.7% 91.7% 3 3 -86.5% 3.7% 3.7% 86.5% -56.4% 58.8% -86.3% 86.3% 4 4 -110.0% 20.0% -20.0% 110.0% -58.0% 58.0% -51.1% 51.1% 1 1 -106.0% 106.0% -106.0% 106.0% -106.0% 106.0% -106.0% 106.0% 21 21 -110.0% 0.9% 6.5% 110.0% -65.0% 66.1% -75.7% 75.7% Silver Reference Laboratory RPD RPD ABS Val 4 4 -68.3% 3.6% 3.6% 68.3% -27.4% 29.1% -22.4% 22.4% 4 4 -93.9% 15.5% -15.5% 93.9% -53.6% 53.6% -52.6% 52.6% 1 1 -75.8% 75.8% -75.8% 75.8% -75.8% 75.8% -75.8% 75.8% 4 4 -57.1% 32.1% -32.1% 57.1% -45.7% 45.7% -46.8% 46.8% 4 4 -20.2% 10.5% -10.5% 20.2% -14.8% 14.8% -14.3% 14.3% 24 24 -106.7% 0.0% 3.6% 106.7% -33.4% 33.7% -18.3% 18.3% E-29 ------- Table E-5. Evaluation of the Effects of Soil Type on RPDs (Accuracy) of Target Elements (Continued) Matrix Sediment Sediment Soil Sediment Soil Site LV RF SB TL WS All Matrix Description Clay /clay loam, salt crust (iron and other precipitate) Silty fine sand (tailings) Coarse sand and gravel (ore and waste rock) Silt and clay (slag- enriched) Coarse sand and gravel (roaster slag) Samples Statistic Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Number Minimum Maximum Mean Median Vanadium Reference Laboratory RPD 5 47.6% 83.3% 65.2% 64.2% 3 74.2% 93.1% 84.8% 87.0% 3 -35.4% 73.8% 17.2% 13.2% ~ ~ ~ ~ 2 50.4% 83.4% 66.9% 66.9% 16 -35.4% 129.5% 65.2% 74.0% RPDABS Val 5 47.6% 83.3% 65.2% 64.2% 3 74.2% 93.1% 84.8% 87.0% 3 13.2% 73.8% 40.8% 35.4% ~ ~ ~ ~ 2 50.4% 83.4% 66.9% 66.9% 16 13.2% 129.5% 69.6% 74.0% Zinc Reference Laboratory RPD 8 -48.4% 48.8% -19.0% -27.4% 13 -63.4% 20.3% -33.2% -38.4% 11 -22.8% 18.9% -3.8% -0.3% 7 -31.3% 70.9% 23.3% 28.5% 7 -51.3% -11.8% -32.5% -24.9% 61 -80.6% 105.7% -19.0% -22.8% RPDABS Val 8 2.1% 48.8% 31.2% 34.2% 13 17.6% 63.4% 39.0% 38.4% 11 0.1% 22.8% 9.3% 7.8% 7 2.3% 70.9% 35.2% 31.3% 7 11.8% 51.3% 32.5% 24.9% 61 0.1% 105.7% 33.0% 32.5% E-30 ------- Table E-5. Evaluation of the Effects of Soil Type on RPDs (Accuracy) of Target Elements (Continued) Site Abbreviations: AS Alton Steel Mill BN Burlington Northern Railroad/ASARCO East CN Naval Surface Warfare Center, Crane Division KP KARS Park - Kennedy Space Center LV Leviathan Mine/Aspen Creek RF Ramsey Flats - Silver Bow Creek SB Sulphur Bank Mercury Mine TL Torch Lake Superfund Site WS Wickes Smelter Site Other Notes: No samples reported by the reference laboratory in this concentration range. Number Number of demonstration samples evaluated. RPD Relative percent difference (raw value). RPD ABS Val Relative percent difference (absolute value). E-31 ------- |