MATERIALS ANALYTICAL REVIEW AND REPORTING SYSTEM

Abstract: A computer-implemented analytical and reporting system (FIG. 1) includes an input device (12), a database (14), and a processor (16). The input device (12) is operative for inputting analytical data results of a test sample. The database includes an analysis methodology data section (14a), and instrument data section (14b), and a forms data section (14c). The processor (16) is operative for receiving from the input device (12) analytical data results of the test sample. The processor is also operative for receiving from the database analysis methodology data of at least one analysis method, instrument data of at least one analytical instrument (14b) and forms data of a desired analytical report form. The processor is also operative for processing the analytical data results and the instrument data using the analysis methodology data (14a) and is operative for generating an analytic report produced on the desired analytical report form depicting final analytical results based on the analysis method and the analytical instrument.

Description: MATERIALS ANALYTICAL REVIEW AND REPORTING SYSTEM [0001] This application is a non-provisional application converted from the provisional application number 60/229,553 filed on August 30, 2000 which is incorporated herein by reference for all purposes. Applicants hereby claim the priority of the provisional application. FIELD OF THE INVENTION [0002] The invention is directed to a materials analytical review and reporting system. More particularly, the invention relates to a computer-implemented materials analytical review and reporting system. BACKGROUND OF THE INVENTION [0003] As a result of their operations, many companies and government- operated facilities produce an effluent that is potentially hazardous to the environment. Federal, state and local governments have passed laws and ordinances regulating such effluent to protect the environment from contamination. As a result, these companies and government-operated facilities must often perform analytical tests on the effluent and report the results to the government agencies. However, there is no standard manner in which to report to the various government agencies. SUMMARY OF THE INVENTION [0004] A computer-implemented analytical and reporting system is hereinafter described. The computer implemented analytical and reporting system of the invention includes an input device, a database and a processor. The input device is operative for inputting analytical data results of a test sample. The database includes an analysis methodology data section, an instrument data section and a forms data section. The analysis methodology data section includes methodology data for conducting at least one analysis method. The instrument data section includes instrument data for modeling at least one analytical instrument. The forms data section includes form data for providing a desired one of a plurality of analytical report forms. [0005] The processor is operative for receiving from the input device the analytical data results of the test sample. The processor is also operative for receiving from the database the analysis methodology data of the at least one analysis method, the instrument data of at least one analytical instrument and the forms data of the desired analytical report form. Further, the processor is operative for processing the analytical data results and instrument data using the analysis methodology data and is operative for generating an analytical report produced on the desired one of the analytical report forms depicting final analytical results based on the at least one analysis method and the at least one analytical instrument. BRIEF DESCRIPTION OF DRAWING [0006] Advantages of the invention will become apparent from the follow description of the exemplary embodiment taken in conjunction with the accompanying drawing in which: [0007] Fig. 1 is a diagrammatical view of the computer-implemented analytical and reporting system of the invention. DETAILED DESCRIPTION OF THE EXEMPLARY EMBODIMENT [0008] As shown in Fig. 1 , a computer-implemented analytical and reporting system 10 of the invention includes an input device 12, a database 14, a processor 16 and an output device 18. The computer-implemented analytical and reporting system 10 of the invention is used for analyzing and reporting the analytical results of a test sample. The input device 12 is operative for inputting analytical data results of the test sample. A skilled artisan would appreciate that the analytical data results of the test sample could be inputted by a conventional computer monitor and keyboard. Alternatively, a skilled artisan would appreciate that the analytical data results can also be provided by an analytical instrument itself, such as a pH meter that can electronically output the pH of a liquid. [0009] The database 14 includes an analysis methodology data section 14a, an instrument data section 14b and a forms data section 14c. The analysis methodology data section 14a includes analysis methodology data for conducting at least one analysis method. The instrument data section 14b includes instrument data for modeling at least one analytical instrument. The forms data section 14c includes forms data for providing a desired one of a plurality of analytical report forms. [0010] The processor 16 is operative for receiving, from the input device 12, the analytical data results of the test sample and is operative for receiving, from the database 14, the analysis methodology data of the at least analysis method, the instrument data of the at least one analytical instrument and the forms data of the desired analytical report form. The processor 16 is also operative for processing the analytical data results and the instrument data using the analysis methodology data. Additionally, the processor 16 is operative for generating an analytical report produced on the desired one of the analytical report forms. The desired one of the analytical report forms is generated by the output device 18. As shown in Fig. 1 , the analytical report form can be displayed on a monitor or can be printed from a printer. Also, a skilled artisan would appreciate that the report can be stored electronically on disk or in a database. In either event, the analytical report form depicts the final analytical results based on the at least one analysis method and the at least one analytical instrument. [0011] The attached documents are incorporated herein by reference for all purposes: 1. EISC's Analytical Review and Reporting Suite, Software for Inorganic and Organic Laboratory Production; 2. MARRS Self-Implement Specifications; 3. Metals Analytical Review and Reporting System - Operating Procedure Version 4.0. [0012] It will be recognized by one of ordinary skill in the art that changes may be made in the above-described embodiment of the invention without departing from the inventive concepts thereof. It is understood, therefore, that the invention is not limited to the particular embodiments disclosed, but is intended to encompass any modifications which are within the scope and spirit of the invention. Environmental Information Systems, Coroσration EISC'S ANALYTICAL REVIEW & REPORTING SUITE Software For Inorganic and Organic Laboratory Production Environmental Information Systems, Corporation 6767 W. Tropicana Avenue Suite 221 Las Vegas, Nevada 89103 www.eisc.net Environmental Information Systems, Corporation TABLE OF CONTENTS Page System Objectives 2 EISC Client Goals (with the system) 3 System Differentiation 4 System Variances ■ Analytical Processes 5 ■ Connectivity to Analytical Instrumentation 9 ■ Processing of Results B Inorganics 10 H Organics 15 System Features ■ Metals Analytical Review & Reporting System 20 ■ General Chemistry Analytical Review & Reporting System 21 ■ Organic Analytical Review & Reporting System: Volatiles 22 ■ Organic Analytical Review & Reporting System: Semi-Volatiles 23 « Organic Analytical Review & Reporting System: Pesticides 24 » Organic Analytical Review & Reporting System: Herbicides and Explosives 25 i t r 1 - * t f r»r / τ. Environmental Information Systems, Corporation fil f EISC'S ANALYTICAL REVIEW & REPORTING SUITE Environmental Information Systems, Corporation's Analytical Review & Reporting Suite software is comprised of six (6) separate modules: ■ Metals Analytical Review & Reporting System ■ General Chemistry Analytical Review & Reporting System ■ Organic Analytical Review & Reporting System: Volatiles ■ Organic Analytical Review & Reporting System: Semi-Volatiles ■ Organic Analytical Review & Reporting System: Pesticides ■ Organic Analytical Review & Reporting System: Herbicides and Explosives ANALYTICAL REVIEW & REPORTING SYSTEM OBJECTIVES B Formalize the reporting of results for inorganic, organic, solid waste, and air analyses. B Make consistent the reporting formats for the labs analytical results. B To meet environmental legislation and regulations established by the federal, regional, state, and local governments ■ Formalize the reporting for legislation such as: the Clean Water Act, Safe Drinking Water Act, Resource Conservation and Recovery Act; Comprehensive Environmental Response, Compensation and Liability Act Superfund Ammendments and ReAuthorization Act, and more. π Formalize results for decision makers for air and water quality standards; air quality control; water supplies; wasterwater disposal; stormwater mgmt.; solid waste; hazardous waste; and general environmental assessments. B Determine the party (ies) responsible for pollution production and its links to potential health effects and sources of contaminants. EISC'S ANALYTICAL REVIEW & REPORTING SUITE EISC: OUR CLIENT'S GOALS Below are listed EISC's clients by category and the goals that they strive to achieve through the use of EISC's Analytical Review & Reporting Systems. B Commercial Laboratories EISC's commercial laboratory clients achieve flexibility in meeting contract laboratory program reporting requirements, as well as, reporting requirements for air force, solid waste, and state and local government; while increasing productivity and maintaining data quality assurance. B DOE Laboratories EISC's DOE laboratory clients strive to achieve the data quality assurance aspect of special mixed waste analysis and special methodology that is only apparent within those specific government locations. a Pharmaceutical Laboratories EISC's pharmaceutical laboratory clients are performing their own pharmaceutical testing, as well as, testing to meet FDA requirements. ■ Environmental Assessment Laboratories EISC's environmental assessment laboratory clients utilize EISC software for the data quality assurance and assessment of a corporation's own waste streams. This includes utility, mining, and petroleum corporations s Food Laboratories EISC's food laboratory clients strive for flexibility in meeting contract laboratory program, air force, solid waste; and Department of Agriculture reporting requirements, while increasing productivity and maintaining data quality assurance. M r pi MFirΗ j /^--; Environmental Information S y stems, Cor p oration EISC'S ANALYTICAL REVIEW & REPORTING SUITE SOFTWARE SYSTEM DIFFERENTIATION EISC's Analytical Review & Reporting Suite is different and superior to all other industry systems for the following reasons: > ■ Provides the flexibility to meet a variety of required formatting requirements without having to change the analytical processes. Currently, no other system possesses the same ability. B Increased productivity of 900% (or 9x's faster) compared to the current industry average. Currently the fastest method of providing analytical review (60 seconds) and reporting (15 minutes). ■ B First and only system to combine both analytical review and reporting within the same software system. ■ First and only commercially available software for General Chemistry. B First and only software system to provide an infinite number of self (user) defined elements. ■ Only metals software to provide both analytical review and client reporting with one system B Only metals software to automatically perform analytical review B Fastest way to review analytical data... only 90-seconds to validate an entire analytical run ■ Only metals software to offer both SW846 and CLP and reporting within one system ■ Only system with the flexibility to generate any type of client specific metals reports and EDD's including SW846, CLP, AFCEE, DOD, DOE, ILCO3.0. « Quickest way to generate all 14 CLP forms... in about 15 minutes B Fully networkable throughout entire laboratory B Will directly connect to a LIMS ■ Easy to implement a First software system to provide AFCEE reporting B First software system to provide SW846 reporting B First software system to provide ILC reporting B First to standardize a reporting format for General Chemistry =*t I ^Y i ^ K - Environmental Information Systems, Corporation EISC'S ANALYTICAL REVIEW & REPORTING SUITE ANALYTICAL REVIEW & REPORTING SUITE VARIANCES EISC's Analytical Review & Reporting Systems essentially operate within the same process flow. The differences occur within the analytical process, connectivity to analytical instrumentation, and processing of results. Analytical Processes Formalize the reporting of results (to decision-makers) pertaining to diseases and their sources. Metals Analytical Review & Reporting System Remainder of this page is intentionally left blank Analytical Processes, cont'd. General Chemistry Analytical Review & Reporting System Organic Analytical Review & Reporting System: Volatiles Analytical Processes, cont'd. Organic Analytical Review & Reporting System: Semi-Volatiles Analytical Processes, cont'd. (Organic: Semi-Volatiles) Organic Analytical Review & Reporting System : Pesticides Organic Analytical Review & Reporting System: HPLC/Explosives Analytical Review & Reporting Suite Variances, cont'd. Connectivity to Analytical Instrumentation Due to the variety of instruments within a laboratory's operations, the Analytical Review & Reporting Systems vary with regards to the connections to these instruments. For instance, the instruments located within an inorganic laboratory differ from those within a General Chemistry laboratory, and so on. Listed below are the EISC modules and their corresponding instrumentation. Metals Analytical Review & Reporting System: Connectivity to : ■ ICP (Inductively Coupled Plasma) ■ ICP/Mass Spectrometry ■ Graphite Furnace Atomic Absorption (GFAA) B Flame Atomic Absorption B Cold Vapor Atomic Absorption ■ Cyanide (latchat) General Chemistry Analytical Review & Reporting System Connectivity to: a Ion Chromatographs ■ Latchat; Mettler Balance ■ Colormetric (Latchat) ■ Conductivity Meter; ' Ion Selective Electrode Analysis B Titrimetric B Total Organic Carbons a Infrared Spectroscopy; Organic Analytical Review & Reporting System: Volatiles Connectivity to: B Gas Chromatograph/Mass Spectrometer B Liquid Chromatograph/Mass Spectrometer ■ Gas Chromatograph Organic Analytical Review & Reporting System: Semi-Volatiles Connectivity to: B Gas Chromatograph/Mass Spectrometer B Liquid Chromatograph/Mass Spectrometer Organic Analytical Review & Reporting System: Pesticides Connectivity to: B Gas Chromatograph B Liquid Chromatograph Organic Analytical Review & Reporting System: Herbacides and Explosives Connectivity to: ■ High Pressure Liquid Chromotagraphy (HPLC) Analytical Review & Reporting Suite Variances, cont'd. Processing of Results. The processing of results differs.in determining the performance of your instruments; contamination within the laboratory; contamination of field equipment; the analytical set-up, the performance of extraction andor performance of digestion, and the testing levels of environmental samples. Processing of Results for Inorganic Systems - Metals Analytical Review & Reporting System - General Chemistry Analytical Review & Reporting System Analytical Sample: Any solution or media introduced into an instrument on which an analysis is performed excluding instrument calibration, initial calibration verification, inintial calibration blank, continuing calibration verification and continiuing calibration blank. Note the following are all defined as analytical samples: undiluted and diluted samples (EPA & non-EPA), predigestion spike samples, duplicated samples, serial dilution samples, analytical spike samples, post-digestion spike samples, interference check samples (ICS), CRDL standard for AA (CRA), CRDL standard for ICP (CRI), laboratory control sample (LCS), preparation blank (PB) and linear range analysis sample (LRS). Analytical Spike: (Inorganic Analysis) The post-digestion spike. The addition of a known amount of standard after digestion. Autozero: (Inorganic Analysis) Zeroing the instrument at the proper wavelength. It is equivalent to running a standard blank with the absorbance set at zero. Average Intensisty (Inorganic Analysis) The average of two different injections (exposures). Background Correction (Inorganic Analysis): A technique to cfompensate for variable background contribution to the instrument signal in the determination of trace elements. Bias Consistent deviation of measured values from the true value, caused by systematic errors in a procedure. Blank (Method Blank) A blank is an artificial sample designed to monitor the intruduction of artifacts into the process. For aqueous samples, reagent water is used as a blank matrix: however, a universal blank matrix does not exist for solid samples, but ometimes clean sand is used as a blank matrix. The blank is taken through the appropriate steps of the porcess. A geagent blenak is an aliquot of analyte-free water or solvent analyzed with the analytical batch Field blanks are aliquotes of analytie-free water or solvent brought to the field in sealed containers and transported back to the laboratory with the sample containers. Trip blanks and equipment blanks are two specific types of field blanks. Trip blanks are not opened in the field. They are a check on sample contamination orginating from sample transport, shipping and from site conditions. Equipment blanks are opened in the field and the contents are poured appropriately over or through the sample collection device, collected in a sample container, and returned to the laboratory as a sample. Equipment blanks are a check on sampling device cleaniness. Calibration (Inorganic Analysis) The establishment of an analytical curve based on the absorbance, emission intensity, or other measured characteristic of known standards. The calibration standards must be prepared using the same type of acid and reagents or concentration of acids as used in the sample preparation. • Processing of Results, Inorganics Calibration Blank (Inorganic Analysis) Usually an organic or aqueous solution that is as free of analyte as possible and prepared with the same volume of chemical reagents used in the preparation of the calibration standards and diluted to the appropriate volume wit the same solvent (water .organic) used in the preparation of the calibration standard. The calibration is used to give the null reading for the instrument response versus concentration calibration curve. Once calibration blank should be analyzed with each analytical batch or every method specified number of samples, whichever is greater. Calibration Check Verification of the ratio of instrument response to analyte amount, a calibration check is done by analyzing for analyte standard in an appropriate solvent. Calibration check solutions are made from a stock solution which is different from the stock used to prepare standards. Calibration Check Standard Standard used to determine the state' of calibration of an instrument between periodic recalibrations. Calibration Standards A series of known standard solutions used by the analyst for calibration of the instrument (i.e. preparation of the analytical curve). Check Sample - A blank which has been spiked with the analyte(s) from an independent source in order to monitor the execution of the analytical method is called a check sample. The level of the spike shall be at the regulation action level when applicable. Otherwise, the spike shall be at 5 times the estimate of the quantification limit. The matrix used shall be phase matched with the samples and well characterized: for example, reagent grade water is appropriate for an aqueous sample. Check Standard- A material of known composition that is analyzed concurrently with test samples to evaluate a measurement process. An analytical standard that is analyzed to verify the calibration of the analytical system. One check standard should be analyzed with each analytical batch or every 20 samples, whichever is greater. (See Calibration Check Standard and Calibration Check) Confidence Coefficient - The probability, % that a measurement result will lie within the confidence interval or between the confidence limits. Confidence Interval Set of possible values within which the true value will lie with a specified level of probability. Confidence Limit One of the boundaries values defining the confidence interval. Continuing Calibration (Inorganic Analysis) Analytical standard run every 10 analytical samples or every 2 hours, whichever is more frequent, verify the calibration of the analytical system. Control Limits A range within which specified measurement results must fall to be compliant. Control limits may be mandatory, requiring corrective action if exceeded, or advisory, requiring that noncompliant data be flagged. Correlation Coefficient A number (r) which indicates the degree of dependence between two variables (concentration - absorbance). The more dependent they are the closer the value to one. Determined on the basis of the least squared line. Processing of Results, Inorganics Duplicate A second aliquot of a sample that is treated the same as the original sample in order to determine the precision of the method. Duplicate Samples Duplicate samples are two separate samples taken from the same source (i.e. in separate containers and analyzed independently. Environmental Sample An environmental sample or field sample is a representative sample of any material (aqueous, nonaqueous, or multimedia) collected from any source for which determination of composition or contamination is requested or required. Environmental samples are normally classified as follows: B Drinking Water - delivered (treated or untreated) water designated as potable water; B Water/Wastewater - raw source waters for public drinking water supplies, ground waters, municipal influents/effluents, and industrial influents/effluents; B Sludge - municipal sludges and industrial sludges; B Waste - aqueous and nonaqueous liquid wastes, chemical solids, contaminated soils, and industrial liquid and solid wastes. Equipment Blank Usually an organic or aqueous solution that is as free of analyte as possible and is transported to the site, opened in the field and poured over or through the sample collection device, collected in the sample container, and returned to the laboratory. This serves as a check on sampling device cleanliness. One equipment blank should be analyzed with each analytical batch or every 20 samples, whichever is greater. GC/EC Gas Chromatography/Electron Capture HRGC High Resolution Gas Chromatography ICS Interference Check Standard Independent Standard A contractor-prepared standard solution that is composed of analytes from a different source than those used in the standards for the initial calibration. Initial Calibration Analysis of analytical standards for a series of different specified concentrations; used to define the linearity and dynamic range of the response of the analytical detector or method. Instrument Calibration Analysis of analytical standards for a series of different specified concentrations; used to define the quantitative response, linearity, and dynamic range of the instrument to target analytes. Instrument Check Sample (Inorganic Analysis) A solution containing both interfering and analyte elements of known concentration that can be used to verify background and interelement correction factors. Instrument Check Standard A multi-element standard of known concenfration prepared by the analyst to monitor and verify instrument performance on a daily basis. Processing of Results, Inorganics Interferents Substances which affect the analysis for the element of interest. Internal Standard(s) Compound(s) added to every standard, blank, matrix spike, matrix spike duplicate, sample (for VOAs) and sample exfract (for semivolatiles) at a known concentration, prior to analysis. Internal Standard(s) are used as the basis for quantitation of the target compounds. Laboratory Control Samples (LCS) A confrol sample of known composition. Aqueous and solid laboratory control samples are analyzed using the same sample preparation, reagents, and analytical methods employed for the EPA samples received. Laboratory Control Standard A standard, usually certified by an outside agency, used to measure the bias in a procedure. For certain constituents and matrixes, use National Institute of Standards and Technology (NIST) Standard Reference Materials when they are available. Linear Range, Linear Dynamic Range (Inorganic Analysis) The concentration range over which the ICP analytical curve remains linear. Matrix Spike (MS) Aliquot of a sample (water or soil) fortified (spiked) with known quantities of specific compounds and subjected to the entire analytical procedure in order to indicate the appropriateness of the method for the matrix by measuring recovery. Matrix Spike Duplicate (MSD) A second aliquot of the same matrix as the matrix spike (above) that is spiked in order to determine the precision of the method. Method Blank An analytical confrol consisting of all reagents, internal standards and surrogate standards, that is carried through the entire analytical procedure. The method blank is used to define the level of laboratory background and reagent contamination. Preparation Blank (reagent blank, method blank) An analytical control that contains distilled, deionized water and reagents, which is carried through the entire analytical procedure (digested and analyzed). An aqueous method blank is treated with the same reagents as a sample with a water matrix. A solid method blank is treated with the same reagents as a soil sample. Quality Control Reference Sample - A sample prepared from an independent standard at a concenfration other than that used for calibration, but within the calibration range. An independent standard is defined as a standard composed of the analyte(s) of interest from a different source than that used in the preparation of standards for use in the standard curve. A quality confrol reference sample is intended as an independent check of technique, methodology, and standards and should be run with every analytical batch or every 20 samples, whichever is greater. This is applicable to all organic and inorganic analyses. Quality Control Sample A solution obtained from an outside source having known concentration values to be used to verify the calibration standards. Random Error The deviation in any step in an analytical procedure that can be explained by standard statistical techniques. Processing of Results, Inorganics Reagent Blank Usually an organic or aqueous solution that is as free of analyte as possible and contains all the reagents in the same volume as used in the processing of the samples. The reagent blank must be carried through the complete sample preparation procedure and contains the same reagent concenfrations in the final solution as in the sample solution used for analysis. The reagent blank is used to correct for possible contamination resulting from the preparation or processing of the sample. One reagent blank should be prepared for every analytical batch or for every 20 samples, whichever is greater. Replicate Sample A replicate sample is a sample prepared by dividing a sample into two or more separate aliquots. Duplicate samples are considered to by two replicates. In cases where aliquoting is impossible, as in the case of volatiles, duplicate samples must be taken for the replicate analysis. Serial Dilution The dilution of a sample by a factor of five. When corrected by the dilution factor, the diluted sample must agree with the original undiluted sample within specified limits. Serial Dilution may reflect the influence of interferents. Target Compound List (TCL) A list of compounds designated by the Statement of Work for analysis. Processing of Results for Organic Systems (All Systems) - Organic Analytical Review & Reporting System: Volatiles - Organic Analytical Review & Reporting System: Semi-Volatiles - Organic Analytical Review & Reporting System:' Pesticides - Organic Analytical Review & Reporting System: Herbicides and Explosives Bar Graph Spectrum: (Organic Analysis) A plot of the mass-to-charge ratio (m e) versus relative intensity of the ion current. Bias Consistent deviation of measured values from the true value, caused by systematic errors in a procedure. Blank (Method Blank) A blank is an artificial sample designed to monitor the introduction of artifacts into the process. For aqueous samples, reagent water is used as a blank matrix: however, a universal blank matrix does not exist for solid samples, but sometimes clean sand is used as a blank matrix. The blank is taken through the appropriate steps of the process. A reagent blank is an aliquot of analyze-free water or solvent analyzed with the analytical batch Field blanks are aliquots of analyte-free water or solvent brought to the field in sealed containers and transported back to the laboratory with the sample containers. Trip blanks and equipment blanks are two specific types of field blanks. Trip blanks are not opened in the field. They are a check on sample contamination orginating from sample transport, shipping and from site conditions. Equipment blanks are opened in the field and the contents are poured appropriately over or through the sample collection device, collected in a sample container, and returned to the laboratory as a sample. Equipment blanks are a check on sampling device cleanliness. 4-Bromoflourobenzene (BFB) (Organic Analysis) Compound chosen to establish mass spectral instrument performance for volatiles analyses. Also used as a surrogate for volatile organic analysis. Calibration Check Verification of the ratio of instrument response to analyte amount, a calibration check is done by analyzing for analyte standard in an appropriate solvent. Calibration check solutions are made from a stock solution which is different from the stock used to prepare standards. Calibration Check Standard Standard used to determine the state of calibration of an instrument between periodic recalibrations. Calibration Standards A series of known standard solutions used by the analyst for calibration of the instrument (i.e. preparation of the analytical curve). CCC: Calibration Check Compound Check Sample A blank which has been spiked with the analyte(s) from an independent source in order to monitor the execution of the analytical method is called a check sample. The level of the spike shall be at the . regulation action level when applicable. Otherwise, the spike shall be at 5 times the estimate of the quantification limit. The matrix used shall be phase matched with the samples and well characterized: for example, reagent grade water is appropriate for an aqueous sample. Check Standard A material of known composition that is analyzed concurrently with test samples to evaluate a measurement process. An analytical standard that is analyzed to verify the calibration of the analytical system. One check standard should be analyzed with each analytical batch or every 20 samples, whichever is greater. (See Calibration Check Standard and Calibration Check) Processing of Results, Organics Confidence Coefficient The probability, % that a measurement result will lie within the confidence interval or between the confidence limits. Confidence Interval Set of possible values within which the true value will lie with a specified level of probability. Confidence Limit One of the boundaries values defining the confidence interval. Continuing Calibration (Organic Analysis) Analytical standard run every 12 hours to verify the calibration of the GC/MS system. Control Limits A range within which specified measurement results must fall to be compliant. Confrol limits may be mandatory, requiring corrective action if exceeded, or advisory, requiring that noncompliant data be flagged. Correlation Coefficient A number (r) which indicates the degree of dependence between two variables (concenfration - absorbance). The more dependent they are the closer the value to one. Determined on the basis of the least squared line. Decafluorotriphenylphosphine (DFTPP) (Organic Analysis) Compound chosen to establish mass spectral instrument performance for semivolatile analysis. Duplicate A second aliquot of a sample that is treated the same as the original sample in order to determine the precision of the method. Duplicate Samples Duplicate samples are two separate samples taken from the same source (i.e. in separate containers and analyzed independently. Environmental Sample An environmental sample or field sample is a representative sample of any material (aqueous, nonaqueous, or multimedia) collected from any source for which determination of composition or contamination is requested or required. Environmental samples are normally classified as follows: " Drinking Water - delivered (treated or untreated) water designated as potable water; B Water Wastewater - raw source waters for public drinking water supplies, ground waters, municipal influents/effluents, and industrial influents/effluents; 8 Sludge - municipal sludges and industrial sludges; B Waste - aqueous and nonaqueous liquid wastes, chemical solids, contaminated soils, and industrial liquid and solid wastes. Equipment Blank Usually an organic or aqueous solution that is as free of analyte as possible and is transported to the site, opened in the field and poured over or through the sample collection device, collected in the sample container, and returned to the laboratory. This serves as a check on sampling device cleanliness. One equipment blank should be analyzed with each analytical batch or every 20 samples, whichever is greater. GC/EC Gas Chromatography/Electron Capture Processing of Results, Organics GC/MS Gas Chromatography/Mass Specfromefry. HRGC High Resolution Gas Chromatography HRMS High Resolution Mass Specfromefry ICS Interference Check Standard Independent Standard A contractor-prepared standard solution that is composed of analytes from a different source than those used in the standards for the initial calibration. Initial Calibration Analysis of analytical standards for a series of different specified concentrations; used to define the linearity and dynamic range of the response of the analytical detector or method. Instrument Calibration Analysis of analytical standards for a series of different specified concentrations; used to define the quantitative response, linearity, and dynamic range of the instrument to target analytes. Instrument Check Sample (Inorganic Analysis) A solution containing both interfering and analyte elements of known concenfration that can be used to verify background and interelement correction factors. Instrument Check Standard A multi-element standard of known concenfration prepared by the analyst to monitor and verify instrument performance on a daily basis. Interferents Substances which affect the analysis for the element of interest. Internal Standard(s) Compound(s) added to every standard, blank, matrix spike, matrix spike duplicate, sample (for VOAs) and sample exfract (for semivolatiles) at a known concentration, prior to analysis. Internal Standard(s) are used as the basis for quantitation of the target compounds. Laboratory Control Samples (LCS) A confrol sample of known composition. Aqueous and solid laboratory confrol samples are analyzed using the same sample preparation, reagents, and analytical methods employed for the EPA samples received. Laboratory Control Standard A standard, usually certified by an outside agency, used to measure the bias in a procedure. For certain constituents and matrixes, use National Institute of Standards and Technology (NIST) Standard Reference Materials when they are available. Matrix Spike (MS) Aliquot of a sample (water or soil) fortified (spiked) with known quantities of specific compounds and subjected to the entire analytical procedure in order to indicate the appropriateness of the method for the matrix by measuring recovery. Matrix Spike Duplicate (MSD) A second aliquot of the same matrix as the matrix spike (above) that is spiked in order to determine the precision of the method. Processing of Results, Organics Method Blank An analytical control consisting of all reagents, internal standards and surrogate standards, that is carried through the entire analytical procedure. The method blank is used to define the level of laboratory background and reagent contamination. Preparation Blank (reagent blank, method blank) An analytical confrol that contains distilled, deionized water and reagents, which is carried through the entire analytical procedure (digested and analyzed). An aqueous method blank is treated with the same reagents as a sample with a water matrix. A solid method blank is treated with the same reagents as a soil sample. Quality Control Reference Sample A sample prepared from an independent standard at a concenfration other than that used for calibration, but within the calibration range. An independent standard is defined as a standard composed of the analyte(s) of interest from a different source than that used in the preparation of standards for use in the standard curve. A quality confrol reference sample is intended as an independent check of technique, methodology, • and standards and should be run with every analytical batch or every 20 samples, whichever is greater. This is applicable to all organic and inorganic analyses. Quality Control Sample A solution obtained from an outside source having known concenfration values to be used to verify the calibration standards. Random Error The deviation in any step in an analytical procedure that can be explained by standard statistical techniques. Reagent Blank Usually an organic or aqueous solution that is as free of analyte as possible and contains all the reagents in the same volume as used in the processing of the samples. The reagent blank must be carried through the complete sample preparation procedure and contains the same reagent concentrations in the final solution as in the sample solution used for analysis. The reagent blank is used to correct for possible contamination resulting from the preparation or processing of the sample. One reagent blank should be prepared for every analytical batch or for every 20 samples, whichever is greater. Replicate Sample A replicate sample is a sample prepared by dividing a sample into two or more separate aliquots. Duplicate samples are considered to by two replicates. In cases where aliquoting is impossible, as in the case of volatiles, duplicate samples must be taken for the replicate analysis. Surrogate Surrogates are organic compounds which are similar to analytes of interest in chemical composition, extraction and chromatography, but which are not normally found in environmental samples. These compounds are spiked into all blanks, calibration and check standards, samples (including duplicates, and QC reference samples) and spiked samples prior to analysis. Percent recoveries are calculated for each surrogate. Surrogate Standard A pure compound added to a sample in the laboratory just before processing so that the overall efficiency of a method can be determined. System Monitoring Compound (Organic Analysis) Compounds added to every blank, sample, matrix spike, matrix spike duplicate, and standard for volatile analysis, and used to evaluate the performance of the entire purge and trap gas chromatograph-mass spectrometer system. These compounds are brominated or deuterated compounds not expected to be detected in environmental media. Processing of Results, Organics Target Compound List (TCL) A list of compounds designated by the Statement of Work for analysis. Tentatively Identified Compounds (TIC) Compounds detected in samples that are not target compounds, internal standards, system-monitoring compounds, or surrogates. Up to 30 peaks (those greater than 10% of peak areas or heights of nearest internal standards) are subjected to mass spectral library searches for tentative identification. TIC - Tentatively Identified Compound Trip Blank - Usually an organic or aqueous solution that is as free of analyte as possible and is transported to the sampling site and returned to the laboratory without being opened. This serves as a check on sample contamination originating from sample transport, shipping, and from the site conditions. One trip blank should be analyzed with each analytical batch or every 20 samples, whichever is greater. Environmental Information Systems, Corporation KISC. EISC's METALS ANALYTICAL REVIEW & REPORTING SYSTEM The following are features of the Metals Analytical Review & Reporting System. FEATURES A. Multiple reporting formats: ' CLP - CLP-Like B SW846 B AFCEE B ILCO3.0 B Any type of client specific reporting B. Additional Reports Generated by MARRS B Instrument reading (raw) result reports B Analytical Run Log Reports B Analytical Review Reports B Special Ad Hoc Reports for Hardness in water * Internal Standard Reports B Exception reports C. User/Self defining reporting lists D. User define QC Criteria E. User Define True Value Lists F. User Define Calculation Strings G. User Define Scientific Significant figures and digits H. Ability to Self Define Review Processes with qualifiers and review messages I. Electronic Exports to various software systems such as Excel and Word J. User Defϊneable methods K. User Defineable Print features L. User Defineabe Uploads M. User Defineable LIMS Connections N. Ability to connect to extraction & digestion software modules O. Ability to connect to an EDD Generator P. System acts as a central repository for control charting * 77 τ > # - f c;- ? - " -Tf Environmental Information Systems, Corporation EISC's GENERAL CHEMISTRY ANALYTICAL REVIEW & REPORTING SYSTEM Following are system features of EISC's General Chemistry Analytical Review & Reporting System. FEATURES A. Multiple reporting formats ■ CLP B CLP-Like B SE846 ■ AFCEE B ILCO3.0 B Any type of client specific reporting B. Additional Reports Generated by MARRS " Instrument reading (raw) result reports ■ Analytical Run Log Reports B Analytical Review Reports B Special Ad Hoc Reports for Hardness in water ■ Internal Standard Reports ■ Exception reports C. User/Self defining reporting lists D. User define QC Criteria E. User Define True Value Lists F. User Define Calculation Strings G. User Define Scientific Significant figures and digits H. Ability to Self Define Review Processes with qualifiers and review messages I. Electronic Exports to various software systems such as Excel and Word J. User Definable methods K. User Definable Print features L. User Definable Uploads M. User Definable LIMS Connections N. Ability to connect to extraction & digestion software modules O. Ability to connect to an EDD Generator P. System acts as a central repository for control charting Environmental Information Systems, Corporation EISC EISC's ORGANIC ANALYTICAL REVIEW & REPORTING SYSTEM: Volatiles Following are system features of EISC's Organic Analytical Review & Reporting System for Volatiles. FEATURES A. Multiple reporting formats: B CLP " CLP-Like " SE846 ■ AFCEE ■ ILCO3.0 B Any type of client specific reporting . B. Additional Reports Generated by MARRS ■ Instrument reading (raw) result reports Analytical Run Log Reports β Analytical Review Reports ■ Special Ad Hoc Reports for Hardness in water ■ Internal Standard Reports Exception reports C. User/Self defining reporting lists D. User define QC Criteria E. User Define True Value Lists F. User Define Calculation Strings G. User Define Scientific Significant figures and digits H. Ability to Self Define Review Processes with qualifiers and review messages I. Electronic Exports to various software systems such as Excel and Word J. User Definable methods K. User Definable Print features L. User Definable Uploads M. User Definable LIMS Connections N. Ability to connect to extraction & digestion software modules O. Ability to connect to an EDD Generator P. System acts as a central repository for control charting f t ri i i z-- ? - Environmental Information Systems, Corporation EISC's ORGANIC ANALYTICAL REVIEW & REPORTING SYSTEM: Semi-Volatiles Following are system features of EISC's Organic Analytical Review & Reporting System for Semi-Volatiles, FEATURES A. Multiple reporting formats: - CLP - CLP-Like « SE846 " AFCEE • ILCO3.0 B Any type of client specific reporting B. Additional Reports Generated by MARRS " Instrument reading (raw) result reports a Analytical Run Log Reports B Analytical Review Reports ■ Special Ad Hoc Reports for Hardness in water B Internal Standard Reports B Exception reports C. User/Self defining reporting lists D. User define QC Criteria E. User Define True Value Lists F. User Define Calculation Strings G. User Define Scientific Significant figures and digits H. Ability to Self Define Review Processes with qualifiers and review messages I. Electronic Exports to various software systems such as Excel and Word J. User Definable methods K. User Definable Print features L. User Definable Uploads M. User Definable LIMS Connections N. Ability to connect to extraction & digestion software modules O. Ability to connect to an EDD Generator P. System acts as a central repository for control charting _. ., ., . „ τ«f — c Environmental Information Systems, Corporation EISC's ORGANIC ANALYTICAL REVIEW & REPORTING SYSTEM: Pesticides Listed below are system features of EISC's Organic Analytical Review & Reporting System for Pesticides. FEATURES A. Multiple reporting formats: B CLP B CLP-Like B SE846 B AFCEE B ILCO3.0 B Any type of client specific reporting B. Additional Reports Generated by MARRS . ■ Instrument reading (raw) result reports " Analytical Run Log Reports B Analytical Review Reports _■ Special Ad Hoc Reports for Hardness in water B Internal Standard Reports B Exception reports C. User/Self defining reporting lists D. User define QC Criteria E. User Define True Value Lists F. User Define Calculation Strings G. User Define Scientific Significant figures and digits H. Ability to Self Define Review Processes with qualifiers and review messages I. Electronic Exports to various software systems such as Excel and Word J. User Definable methods K. User Definable Print features L. User Definable Uploads M. User Definable LE IS Connections N. Ability to connect to extraction & digestion software modules O. Ability to connect to an EDD Generator P. System acts as a central repository for control charting Environmental Information Systems, Corporation EISC's ORGANIC ANALYTICAL REVTEW & REPORTING SYSTEM: Explosives Listed below are system features of EISC's Organic Analytical Review & Reporting System for Explosives. FEATURES A. Multiple reporting formats: B CLP - CLP-Like ■ SE846 B AFCEE ■ ILCO3.0 B Any type of client specific reporting B. Additional Reports Generated by MARRS B Instrument reading (raw) result reports B Analytical Run Log Reports 0 Analytical Review Reports ■ Special Ad Hoc Reports for Hardness in water * Internal Standard Reports B Exception reports C. User/Self defining reporting lists D. User define QC Criteria E. User Define True Value Lists F. User Define Calculation Strings G. User Define Scientific Significant figures and digits H. Ability to Self Define Review Processes with qualifiers and review messages I. Electronic Exports to various software systems such as Excel and Word J. User Definable methods K. User Definable Print features L. User Definable Uploads M. User Definable LIMS Connections N. Ability to connect to extraction & digestion software modules O. Ability to connect to an EDD Generator P. System acts as a central repository for control charting " EISC Environm ental Ir lform ation System s, Corpo ration Metals Analytical Review & Reporting System Process Flow Chart- Version 4.0 Review Results at the Analytical Run Level and at the Sample Results Level Make any Changes and Recalc if necessary. Print Analytical Review I Save Analytical Run Go To Reporting [EISC Environm ental Inform ation System s, Corporation © Copyright 1999, Environmental Information Systems, Corporation. All rights reserved. Unauthorized duplication is a violation of applicable laws. Environmental Information Systems, Corporation EISC List of Acronyms and Abbreviations AA Atomic Absorption ABS Absorbance CLP Contract Laboratory Program CCV Continuing Calibration Verification CCB Continuing Calibration Blank EPA Environmental Protection Agency GFAA Graphite Furnace Atomic Absorption ICP Inductively Coupled Plasma ICP-MS Inductively Coupled Plasma - mass spectroscopy ICV Initial Calibration Verification ICB Initial Calibration Blank ICS Interference Check Standard DDL Instrument Detection Limit ID Identification IS Internal Standard LDR Linear Dynamic Range LCS Laboratory Control Sample DL Method Detection Limit MS Matrix Spike MSD Matrix Spike Duplicate ppb parts per billion ppm parts per million PQL Practical Quantitation Limit QA Quality Assurance QC Quality Control R Recovery RDL Reporting Detection Limit RPD Relative Percent Difference SDG Sample Delivery Group SOW Statement of Work STLC Soluble Threshold Limit Concentration TCLP Toxicity Characteristic Leaching Procedure TV True Value MARRS Self-Implement Specifications MARRS Self-Implementor Send Client Self -Implementor Client Receives Self-Implementor With Instructions to Install Book on Self Implementor, Time Disabler Installation User Installs Self-Implementor Counter User Starts Self-Implementor Questions Group 1 Lab Name and Lab Cede Questions Group 2 General Information Group 2- Number of Instruments and Instrument Category Group 2- Key Code Group .2- Select Reporting Modules Group 2- Select Matrices Group 2- Jlnter Directory Paths Questions Group 3 Instruments Group 3- Enter Instrument Information Group 3- Enter Initials and Finals Group 3- Edit Analyte List Group 3- -Enter Standard Reporting List Back to Group 3- Copy Reporting Lists Group 3 Group 3- Enter QC Criteria Lists -Group 3- Copy QC Criteria Lists Group 3- Enter True Values Lists Group 3- Copy True Values Lists Group 4- Enter EEC's Group 4- Edit Naming Conventions MARRS Self-Implementor Specifications Items that need to be defined. 1 Lab Name and Lab Abbreviation 2 General Information Number of Instruements for Instrument Category Key Code Select Reporting Modules Select Matrices Enter Directory Paths 3 Instruments Enter Instrument Information Enter Initial and Final Volumes Edit Analyte List Enter Standard Reporting List Copy Reporting List Enter Standard QC Criteria List Copy QC Criteria List Enter Standard Truevalue List Copy Truevalue List 4 More Instrument Information Enter IEC's (Just for ICP's) Edit Sample Naming Conventions Important Items: Self Implementor is installed and walks user through a story book. Save the Profile of the client (Report) Add Default Profile Steps to Self-Implement 1. Users Receives Self-Implementor CD, Instructions to install self-implementor, Possible book on self-implementor with different options, Embedded Time Disabler, and Installation Counter. 2. User Installs self-implementor 3. User Starts Self-Implementor Questions Group #1 - How do you want your lab name to appear on the Reports and what Lab Code do you want to go by? Present Clients: Lab Code Lab Name on Reports EISC EISC Laboratories, Inc. Ceimic Ceimic Laboratories CompuChem CompuChem Eckenfelder Eckenfelder Laboratories or E-Labs En Chem En Chem Laboratories Envirotech STL-Envirotech GEL General Engineering Laboratories, Inc. GPL GPL Laboratories, LLLP. Jacksonville Columbia Analytical Services Kelso Columbia Analytical Services LLNL Lawrence Livermore National Laboratory Merck Merck Laboratories QC Inc. QC Laboratories Redding Columbia Analytical Services Rochester Columbia Analytical Services Rocky Flats Rocky Flats Plant Laboratory Savannah STL-Savannah STLBALT STL-Baltimore Hanford WSCF 5. Questions Group #2 - General Information - Please Enter the number of instruments for each instrument category? Present Instrument Categories: ICP(s), CVAA(s), GFAA(s), Cyanide(s), ICPMS(s) Present Layout of Client Base: Client ICP(s) CVAA(s) GFAA(s) Cyan(s) ICPMS(s Ceimic 2 1 0 CompuChem 2 1 0 Eckenfelder 1 1 0 En Chem 2 1 1 Envirotech 3 2 0 GEL 2 2 0 1 GPL 1 1 4 1 0 Jacksonville 1 2 2 0 1 Kelso 2 1 3 0 1 LLNL 1 1 1 0 0 Merck 2 1 1 0 0 QC Inc. 2 1 3 0 0 Redding 1 1 3 0 0 Rochester 3 1 2 0 0 Rocky Flats 1 1 0 0 0 Savannah 4 1 5 1 0 STLBALT 4 1 2 1 0 Hanford 1 1 0 0 2 Questions Group #2 - General Information - Enter Keycode found on CD Case. This will detemiine how many Reporting Modules the Client can select, the duration before the system will not be functional (We will send them a key code that opens the system up to never be disabled when they pay), and number of installations allowed. 7. Questions Group #2 Select Reporting Modules to include MARRS Installation. (Two is the norm) Present Systems can contain: CLP ILM4.0 (client also gets Hybrid with this one). SW-846 CLP ILC3.0 AFCEE Module DOD Module WEPP Module DOE Module Questions Group #2 - Select Matrices that you will run within MARRS. Unique Matrices run wi thin MARRS: Matrix Matrix Category Units Unit Conversion WATER LIQUID ug/L 1 SOIL SOLID mg/kg 0.001 TCLP LIQUID ug/L 1 PE SOIL SOLID mg/kg 0.001 SEDIMENT SOLID mg kg 0.001 OIL SOLID mg/kg 0.001 TISSUE SOLID mg kg 0.001 AIR AIR ug/Filter 1 STLC LIQUID ug/L 1 WIPES AIR ug/Swipe 1 SLUDGE SOLID mg/kg 0.001 SOLID SOLID mg/kg 0.001 LIQUID LIQUID ug/L 1 NON-AQUEOUS SOLID mg/kg 0.001 OIL SOLID mg kg 0.001 FILTERS SOLED mg/kg 0.001 DRINKH20 LIQUID ug/L 1 WASTEH20 LIQUID ug/L 1 SOBL/SEDIMENT SOLID mg/kg 0.001 DISSOLVED LIQUD ug/L 1 BIOTA SOLID mg/kg 0.001 DRINKING WATER LIQUID ug/L 1 ORGANIC LIQUID ug/L 1 SPLP LIQUID ug/L 1 SWIPES AER ug/Swipe 1 H20 LIQUID ug/L 1 OTHER LIQUID ug L 1 MISC SOLED mg/kg 0.001 LEACHATE LIQUID ug/L 1 SYNTHETIC LEACHATELIQUID ug/L 1 SWAB SOLID ug/swab 10 ELLUTRIATE LIQUID ug/L 1 AVSSEM LIQUID ug L 1 PAINT SOLED mg/kg 0.001 . Questions Group #2 - Enter the Directory Paths where you will want to store or locate files. (Directory Paths of Instrument Files will come later) MARRS Item(s) Default Directory MARRS Reports C:\Datarev\Crreports MARRS Reference Data C:\Datarev\DBS (Matrices, Naming Conventions, Reports, Elements, ...) LEMS File(s) Location C:\Datarev\Data MARRS Lists C:\Datarev\QCDBS (Reporting, QC Criteria, Truevalue, EEC's ...) Saving Finished SDG C:\Datarev\SDG Location Percent Solids Location C:\Datarev\Data 10. Questions Group #3 - Based on the Number of Instruments that were selected during Questions Group #2 this screen should look something like this in a grid format. Enter Name of Inst Name of Inst Files Located Instrument Make on Screen on Reports Upload (YIN) in what Dir Path ICPl ICP2 CVAAl GFAA1 GFAA2 GFAA3 Cyanide 1 ICPMS1 Continued from the Split Screen in the Grid Number File 1 File 2 LED Method If Manual Instrument of Files Filter Filter to se on Rpts Time Seq between Samples ICPl ICP2 CVAAl GFAA1 GFAA2 GFAA3 Cyanide 1 ICPMS1 Different ICP Makes TJA61 ICP TJA61 Trace ICP TJ ICP-OES TJA Iris ICP TJA36 Enviro ICP PE Optima ICP Leeman ICP JY48P ICP JY24 ICP JY5 ICP Different CVAA Makes Leeman CVAA PE CVAA Cetac Hg Analyzer Varian FAA/CVAA Different GFAA Makes PE 4100 GFAA PE 5100 GFAA MultiPro Varian Flame AA Varian GFAA Hydride E-10 TJA 22 GFAA TJA 4000 GFAA Different Cyanide Makes Lachat MultiPro Different ICPMS Makes HP ICPMS PE ICPMS VG ICPMS Different LED Methods P ICP AV CVAA CV CVAA H Hydride GFAA F GFAA A Flame AA AS Cyanide C Cyanide CA Cyanide MS ICPMS 1. Questions Group #3 - Based on the Matrix and Instruments selected by the User they should see a grid containing the following: Instrument ICPl ICP2 CVAA GFAA Cyanide ICPMS .... Matrix Ential Final Initial Final WATER 50 50 50 50 SOEL 1 100 1 200 TCLP 1 1 1 1 SPLP 100 100 100 100 12. Questions Group #3 - Bring basic Analyte List over from User Selection of Instruments- Elements need to match with the Instrument exactly. Report Name ICP's CVAA GFAA Cyanide Ag Silver 7440-22-4 Ag3280 Al Aluminum 7429-90-5 A13082 As Arsenic 7440-38-2 As 1890 As Au Gold B Boron 7440-42-8 B 2496 Ba Barium 7440-39-3 Ba4396 Be Beryllium 7440-41-7 Be3130 Bi Bismuth 7740-69-9 Ca Calcium 7440-70-2 Ca3179 Cd Cadmium 7440-43-9 Cd2265 Cn Cyanide Cn Co Cobalt . 7440-48-4 Co2286 Cr Chromium 7440-47-3 .Q-2677 Cu Copper 7440-50-8 Cu3247 Cu Fe Iron 7439-89-6 Fe2714 Hg Mercury 7439-97-6 Hg K Potassium 7440-09-7 K_7664 Li Lithium 7439-93-2 Mg Magnesium 7439-95-4 Mg2790 Mn Manganese 7439-96-5 Mn2576 Mo Molybdenum 7439-98-7 Mo2020 Na Sodium 7440-23-5 Na3302 Ni Nickel 7440-02-0 Ni23l6 Os Osmium P Phosphorus 7440-00-0 P 1782 Pb Lead 7439-92-1 Pb2203 Pb Pb2203/1 Pb2203/2 Pd Palladium Pt Platinum Pu Plutomium S Sulfur 7441-22-9 Sb Antimony 7440-36-0 Sb2068 Sb Sb2068/1 Sb2068/2 Se Selenium 7782-49-2 Sel960 Se Sel960/1 Sel960/2 Si Silicon 7440-31-5 Sn Tin Snl899 Sn Sr Strontium 7440-24-6 Sr4215 Ti Titanium 7440-32-6 Ti3349 Tl Thallium 7440-28-0 T11908 Tl U Uranium 7440-61-1 V Vanadium 7440-62-2 V 2924 Y Yitrium Y Zn Zinc 7440-66-6 Zn2138 Report Name ICPMS Ag Silver 7440-22-4 Ag 107 Al Aluminum 7429-90-5 Al 27 As Arsenic 7440-38-2 As 75 Au Gold Au 197 B Boron 7440-42-8 B 11 Ba Barium 7440-39-3 Ba 137 Be Beryllium 7440-41-7 Be_9 Bi Bismuth 7740-69-9 Ca Calcium 7440-70-2 Ca 44 Cd Cadmium 7440-43-9 Cd_l l l Cn Cyanide Co Cobalt 7440-48-4 Co 59 Cr Chromium 7440-47-3 Cr 52 Cs Cesium Cs 133 Cu Copper 7440-50-8 Cu 65 Fe Iron 7439-89-6 Fe 57 Hg Mercury 7439-97-6 Hg 199 Hg 200 Hg 202 Ir Ir 193 K Potassium 7440-09-7 K 39 Li Lithium 7439-93-2 Li 7 Mg Magnesium 7439-95-4 Mg 24 Mn Manganese 7439-96-5 Mn 55 Mo Molybdenum 7439-98-7 Mo 95 Na Sodium 7440-23-5 Na 23 Nb Nb 93 Ni Nickel 7440-02-0 Ni 60 Os Osmium Os 193 P Phosphorus 7440-00-0 P 31 Pb Lead 7439-92-1 Pb 206 Pd Palladium Pd 105 Pt Platinum Pt_195 Pu Plutomium Re Re 185 Rh Rh 103 Ru Ru_101 S Sulfur 7441-22-9 Sb Antimony 7440-36-0 Sb 121 Se Selenium 7782-49-2 Se 82 Si Silicon 7440-31-5 Si 28 Sn Tin Sn 118 Sr Strontium 7440-24-6 Sr 86 Th Thorium Th 232 Ti Titanium 7440-32-6 Ti~49 Tl Thallium 7440-28-0 Tl 205 U Uranium 7440-61-1 U 238 V Vanadium 7440-62-2 V 51 Y Yitrium Y Zn Zinc 7440-66-6 Zn 66 Zr Zirconium Zr 90 13. Questions Group #4 - Enter the following information to create a Standard Reporting List. You will be asked if you want to copy this list to make other Reporting Lists right after creation of this list. The Elements from the question above will be used for the list Enter a name for the Reporting List: Enter RDL values and other pertinent information into the following list: Present the following information in a split screen grid. RDL Reported Method/ TCLP STLC (Default to Yes) Test Code ' Reg Limit Reg Limit Ag3280 A13082 As 1890 B_2496 Ba4396 Be3130 Ca3179 Cd2265 Co2286 Cr2677 Cu3247 Fe2714 K. 7664 Mg2790 Mri2576 Mo2020 Na3302 N.2316 P_1782 Pb2203 Pb2203/1 Pb2203/2 Sb2068 Sb2Q68/l Sb2068/2 Sel960 Sel960/1 Sel960/2 Snl899 Sr4215 Ti3349 T11908 V 2924 Y Zn2138 Units Wavelength (Default to ppb) (Default to Values) Background Ag3280 A13082 As 1890 B 2496 Ba4396 Be3130 Ca3179 Cd2265 Co2286 Cr2677 Cu3247 Fe2714 K 7664 Mg2790 Mn2576 Mo2020 Na3302 Ni2316 P_1782 Pb2203 Pb2203/1 Pb2203/2 Sb2068 Sb2068/1 Sb2068/2 Sel960 Sel960/1 Se 1960/2 Snl899 Sr4215 Ti3349 Til 908 V_2924 Y Zn2138 14. Questions Group #4 - Do you want to make more Reporting Lists. You can copy or make them as you did the Standard Reporting List. 15. Questions Group #4 - Enter the following information to create a Standard QC Criteria List. You will be asked if you want to copy this list to make other QC Criteria Lists right after creation of this list. Enter a name for the QC Criteria List: Enter QC Criteria values into the following list: Present the following information in a split screen grid. CCV Crit ICV Crit ICSA Crit ICSAB Crit (+/- 100%) (+/- 100%) (+/- 100%) (+/- 100%) Ag3280 A13082 As 1890 B_2496 Ba4396 Be3130 Ca 179 Cd2265 Co2286 Cr2677 Cu3247 Fe2714 K_7664 Mg2790 Mn2576 Mo2020 Na3302 Ni2316 P_1782 Pb2203 Pb2203/1 Pb2203/2 Sb2068 Sb2068/1 Sb2068/2 Sel960 Sel960/1 Sel960/2 Snl899 Sr4215 Ti3349 T11908 V_2924 Y Zn2138 LCSW Low LCSW High LCSS Low LCSS High (%) (mg kg) (mg/kg) Ag3280 A13082 As 1890 B_2496 Ba4396 Be3130 Ca3179 Cd2265 Co2286 Cr2677 Cu3247 Fe2714 K 7664 Mg2790 Mn2576 Mo2020 Na3302 N-2316 P_1782 Pb2203 Pb2203/1 Pb2203/2 Sb2068 Sb2068/1 Sb2068/2 Sel960 Se 1960/1 Se 1960/2 Snl899 Sr4215 Ti3349 Til 908 V_2924 Y Zn2138 LRA Crit MS Low MS High PDMS Low (+/■ 100%) Yo) Ag3280 A13082 As 1890 B_2496 Ba4396 Be3130 Ca3179 Cd2265 Co2286 Cr2677 Cu3247 Fe2714 K_7664 Mg2790 Mn2576 Mo2020 Na3302 Ni2316 P_1782 Pb2203 Pb2203/1 Pb2203/2 Sb2068 Sb2068/1 Sb2068/2 Sel960 Se 1960/1 Se 1960/2 Snl899 Sr4215 Ti3349 T11908 V_2924 Y Zn2138 PDMS High Dup Crit Ser Dil Crit (%) (%) Ag3280 A13082 As 1890 B_2496 Ba4396 Be3130 Ca3179 Cd2265 Co2286 Cr2677 Cu3247 Fe2714 K_7664 Mg2790 Mn2576 Mo2020 Na3302 Ni2316 P_1782 Pb2203 Pb2203/1 Pb2203/2 Sb2068 Sb2068/1 Sb2068/2 Sel960 Sel960/1 Se 1960/2 Snl899 Sr4215 Ti3349 T11908 V_2924 Y Zn2138 15. Questions Group #4 - Do you want to make more QC Criteria Lists. You can copy or make them as you did the Standard QC Criteria List. 16. Questions Group #4 - Enter the following information to create a Standard Truevalue List. You will be asked if you want to copy this list to make other Truevalue Lists right after creation of this list. Enter a name for the Truevalue List: Enter EDL Date for List: Enter LDR Date for List: Enter ICAL Source for List: Enter CCAL Source for List: Enter ICS Source for List: Enter CRDL Source for List: Enter LCS Solid Source for List: Enter LCS Liquid Source for List: Enter Truevalue values into the following list: Present the following information in a split screen grid. CCV ICV CRI/CRA ICSA ICSAB LCSW LCSS LRA Ag3280 A13082 Asl890 B_2496 Ba4396 Be3130 Ca3179 Cd2265 Co2286 Cr2677 Cu3247 Fe2714 K 7664 Mg2790 Mn2576 Mo2020 Na3302 Ni2316 P 782 Pb2203 Pb2203/1 Pb2203/2 Sb2068 Sb2068/1 Sb2068/2 Sel960 Sel960/1 Se 1960/2 Snl899 Sr4215 T11908 V_2924 Y Zn2138 MS PDMS EDL HIGHSTD LDR TEME UNITS Ag3280 A13082 Asl890 B_2496 Ba4396 Be3130 Ca3179 Cd2265 Co2286 Cr2677 Cu3247 Fe2714 K_7664 Mg2790 Mn2576 Mo2020 Na3302 Ni2316 P_1782 Pb2203 Pb2203/1 Pb2203/2 Sb2068 Sb2068/1 Sb2068/2 Sel960 Sel960/1 Sel960/2 Snl899 Sr4215 Ti3349 TH 908 V_2924 Y Zn2138 16. Questions Group #4 - Do you want to make more Truevalue Lists. You can copy or make them as you did the Standard Truevalue List. 17. Questions Group #4 - Enter an IEC Date and Select the elements to fill top columns of IEC Table. Enter Wavelength if you wish for the Analyte to appear on the Rows of IEC. See Attachment for details. 18. Questions Group #4 - The following is default list of Naming Conventions of Samples coming From the instrument to be converted to a particular QC Type. Please change the Character String where appropriate. Return Embedded Char String Num of Chars QC Type Matrix Suffix Seq N STD 3 CAL WATER Y N N ICV 3 ICV WATER Y Y N CCV 3 CCV WATER Y Y N ICB 3 ICB WATER Y Y N CCB 3 CCB WATER Y Y N CRI 3 CRDL WATER Y Y N ICSA 4 ICSA WATER Y Y N ICSAB 5 " ICSAB WATER Y Y Y LCSW 4 LCS WATER Y N Y LCSS 4 LCS SOE Y N Y LCSWD 5 LCSD WATER Y N Y LCSSD 5 LCSD SOEL Y N Y MBW 3 MB WATER Y N Y MBS 3 MB SOIL Y N Y MSD 3 MSD WATER Y N Y MS 2 MS WATER Y N Y PS 2 AS WATER Y N N LRA 3 LRA WATER Y N Y DUP 3 DUP WATER Y N Y PSD 3 ASD WATER Y N Y SD 2 SD WATER Y N N PQL 3 PQLLOW WATER Y N N RB 2 RB WATER Y N Groups 3 and 4 get repeated for each Instrument. Items to leave out of the User Question setup but are set during Generation of the Tables are the followmg: Additional Ad-Hoc Lab Reports Sig Fig Lists Other Flagging Criteria Items that will be addressed by writing specifications next week are the following: System Switches Uploads LIMS Connection (Prep) LEMS Connection (Manual) 52 53 Environmental Information Systems, Corporation Metals Analytical Review and Reporting System - Operating Procedure Version 4.0 Analytical Result Upload and Review From the Analytical Method list, select a method. Next, click on Analytical and then Result Upload and Review. If only Manual Entry and Review appears, then you have selected a method for which upload files are not available or have not been configured for in t he system. Once you have clicked on Result upload and Review, you will he presented with five folders; Select Instrument Files, Begin Upload, Associate Lists, Process Results, and Review Results. These five folders make up the Analytical Result Upload and Review section of the system. It is in this section that we upload our files, assign the appropriate QC and reporting lists, process, and then review the results.- The process we follow to build analytical runs and/or SDGs flows from left to nght and begins with the folder Select Instrument Files. From this screen, select the path in the network where the folders are located (a default path will be set for each individual instrument) and then select the instrument files from the column just to the right. Consecutive files may be selected using the shift key (keyboard) or individually while holding down the Ctrl key. Once you have selected the file(s) to be uploaded, click on the " -V to populate the Selected Instrument(s) columns. You may de-select files by clicking on "<-". Once the instrument files have been selected, continue on to folder Begin Upload. Next, click on the Begin Upload button located at the bottom of the screen and watch as the instrument files are upload. You have two other options in this folder, Print Raw Results Report and Print Runlog Report. The Raw Results Report is a summary of the data being uploaded from the instrument file; sample ED, parameter, result, analysis date and time, dilution factor and data file. The Runlog report is a list of the samples within the file, in analytical order, along with the date/time of analysis, dilution factor, matrix, data file and batch number. This can be either printed and/or reviewed on the screen and is often used in place of handwritten runlogs. Once you have uploaded the files and printed the necessary reports, it's time to move on to the Associate Lists folder. Here is where you will select the Reporting Lists, QC Criteria Lists, True Value Lists, Review and Qualifier Lists, Calculation Process Lists, Sig Figure Digits Lists and Print Set Up Lists that you want to associate with the samples being processed. Before we begin associating lists, lets look at the folder. In the folder you will see columns with the headers Sample ID, Client ID, Ana date, Time, DU, Matrix, Initial, Final, % Solids, Z flag and the default lists which are currently being associated with the samples. At the bottom of the screen, you will see three windows with the headers Reporting List, QC Criteria List and True Value List To change any one of the current lists, highhght one with your mouse and click on the Reset button below The columns will reflect the change, (to see what fields each list contains, see Lists Details starting on page 14) To edit these lists, create new ones, or assign lists at a sample level, click on the appropriate list in the bottom left hand corner of the folder. To edit an existing list, highlight the list of choice in the window on the left and then make the necessary adjustments (remember, all edits are permanent). To create a new list, simply click on Add New list Set, enter a name, select one of the existing hsts to copy, click on Copy List, and then click on Return to List Review. Be sure to highlight the list of concern prior to making any edits to assure you are changing the correct list To select a list at the sample level, simply click on Select List at a Sample Level, select a list, highlight the samples of interest, and click on Set List When you are finished, return to the previous screen and then return again to the main folder. While you are in the Associate Lists folder you can also Select a Matrix, Z out samples, Select De-Select samples for the run, set the Initial Wt/Final Volume, Batch Samples, get Client hub, Select the Rounding Type (CLP Odd/Even or Mathematical), and select the Low Reporting Limit (MDL/TDL). When you are satisfied with the lists you have chosen, move on to the Process Results folder. By clicking on Process Results, you will be initiating the system to apply the hsts you have chosen to the instrument files initially uploaded Build Review Tables builds the tables needed to review forms. Once the results have been successfully processed, it is time to review the results in the folder Review Results. Here you can perform a preliminary review of the analytical run before saving it to a file for the reporting department You can also review all results. The related sample information appears when a QC Sample is selected to review. However, if you make any changes be sure to click on the Re-Calc button in the bottom right hand comer to apply the changes Once satisfied with the results you can save the processed file to an analytical run by clicking on Save Analytical Run. One important note, because the folders go left to right does not mean you can not go back if an error is made. However, if you do go back you must once again repeat the appropriate steps to insure the changes that you have made are applied. An Analytical Review Report can be printed from this folder. This report contains the Sample ED, Parameter, Duution Factor, PASS/FAIL, Raw Result, Matrix, Recovery, QC Criteria, RPD, Analytical Date, Umts, Initial and Fmal Volume Manual Entry and Review When you select a method from the Analytical Method List that is not configured for instrument uploads, you will be required to create the SDG through the Manual Entry and Review Section. To perform this process select a method, click on Analytical, and then click on Manual Entry and Review. As was the case with the Analytical Results Upload and Review section, this section is also made up of five folders: Build Analytical Run, Enter Concentrations, Associate Lists, Process Results, and Review Results. In the first folder, Build Analytical Run, you will retrieve the necessary samples from the L S, enter the appropriate information, and build your analytical mn in the order in which the samples are analyzed. Choose whether the samples analyzed are listed by time or sequence, the total number of samples in the run, Date, start time, time span between samples (in seconds), operator initials, and run number. You can then build the run by clicking over the QC Types and Sample ID's. Once you have built the run, click on Commit Run for Entry. In the Next folder, Enter Concentrations, is where the concentrations for each sample are entered. Once you have entered the necessary data on the selected screen, click on Loading Manual Entry to load the results. 3. Once the results have been successfully loaded, move on to the Associate Lists folder. The next three folders work the same as when uploading results. Here is where you will select the Reporting Lists, QC Criteria Lists, True Value Lists, Review and Qualifier Lists, Calculation Process Lists, Sig Figure/Digits Lists and Print Set Up Lists that you want to associate with the samples being processed. Before we begin associating lists, lets look at the folder. In the folder you will see columns with the headers Sample ID, Client ID, Ana date, Time, Dil, NIatrix, Initial, Final, % Solids, Z flag and the default lists which are currenuy being associated with the samples. At the bottom of the screen, you will see three windows with the headers Reporting List, QC Criteria List and True Value List To change any one of the current lists, ghlight one with your mouse and click on the Reset button below. The columns will reflect the change. To edit this list, create new ones, or assign lists at a sample level, click on the appropriate list in the bottom left hand comer of the folder. To edit an existing list, highlight the list of choice in the window on the left and then make the necessary adjustments (remember, all edits are permanent). To create a new list, simply click on Add New List Set, enter a name, select one of the existing lists to copy, click on Copy List, and then click on Return to List Review. Be sure to highlight the list of concern prior to making any edits to assure you are changing the correct list To select a list at the sample level, simply click on Select List at a Sample Level, select a list, higMight the samples of interest and click on Set List When you are finished, return to the previous screen and then return again to the main folder. While you are in the Associate Lists folder you can also Select a Matrix, Z out samples, Select/De-Select samples for the run, set the Initial Wt/Final Volume, Batch Samples, get Client Info, Select the Rounding Type (CLP Odd Even or Mathematical), and select the Low Reporting Limit (MDL/TOL). 4. When you are satisfied with the hsts you have chosen, move on to the Process Results folder. By clicking on Process Results, you will be initiating the system to apply the hsts you have chosen to the instrument files previously uploaded. Build Review Tables builds the tables needed to review forms. 5. Once the results have been successfully processed, it is time to review the results in the folder Review Results. Here you can perform a preliroinary review of the analytical run before saving it to a file for the reporting department. You can also review all results. The related sample information appears when a QC Sample is selected to review. However, if you make any changes be sure to click on the Re-Calc button in the bottom right hand corner to apply the changes. Reporting Section The reporting section can be accessed by clicking on the Go to reporting button located at the top of the screen within the Analytical Result Upload and Review section as well as in the Manual Entry and Review Screen. As was the case with the analytical sections, you are once again presented with five folders: Prep Information, Select/De-Select Elements, Edit Results, Report(s), and Exception Reports. I . The first folder in the reporting process is the Prep Information folder. The following tasks can be performed within this folder (buttons in bold print)' • Retrieve Client Info from the LIMS system o Adjust the Matrices. • Set Date Collected and or Date Received. • Sample Batching. » Adjust QC Types. » Set Run Numbers (analytical) β 21-FIag samples not being reported. • Set Analytical Date • Select/De-Select Samples . Re-Sequence ICV's, ICB's, CCV's and CCB's All of the above parameters are set in the same manner Chck on the button, select the parameter to be set, highlight the associated sample, set, and return. Once again it is important to chck on the Re-Process/Re-calc button any time changes have been made to insure that the changes will be applied to the final results 2. The next folder is Select/De-Select Elem. Analytes are selected and de-selected here atthe sample level. A good example is an ICP with multiple analytes being reported with each individual analysis. All the analytes may not be reported from the same analysis depending on dilutions and other quality control issues This screen allows you to select which analyte(s) you want to report from which analyses. Once you are satisfied that all the samples and QC are be g associated properly, you can move on to the Edit Results folder Here you can perform a thorough review of the results that are to be reported on the forms to be selected. Parameter hsts, ckhmon factors, collection and receipt dates EDLs, RDLs, %R and RPDs are just some of the data that can he reviewed and edited, if necessary, within this folder. To perform global changes (those which effect all the samples) click on Run Adjustments and make changes to one or all of the following parameters. IDL Values MDL Values RDL Values Instrument Units Report Units Unit Conversion TCLP Reg Limits Sig Figs and Sig Digits Main Parameter Report Method LDR, Lid Method and Instrument Once again, be sure to chck on Re-Calc and Rebuild Review Tables to insure that and adjustments that have been made will be applied to the final results. When all the results and parameters have been successfully reviewed you can move on to the Report(s) folder Before printing the necessary forms and saving the SDG, you will want to look at the following: • Report Headers - Enter the SDG No., Client Name, Contract Project, Lab Code, Case No., SAS No , Method, SOW No , Level, Report Header, Report Footer, and SDG Comments. Choose the ffigh and Low Reporting Limits, and whether you want Client ID's or Lab ID's reported on Forms 8, 13 and 14. • Select Samples for Z out - Select samples that are not associated with the SDG for which you do not want Form l's processed and would like Z' d out on the Run Log • Select Samples in Run - Select samples and QC to be reported. • Sample Comments - These are comments made at the sample level, which will appear on the appropriate Form 1 ' s β Color, Clarity and Texture - Which will appear on the appropriate Form 1 ' s. • Edit MSA's or IEC s β Review Sources - For forms 2a, 2b, 4, and 7. • Update Parameters at an SDG level. • Direct Form Edit You are now ready to print and/or review the selected forms by clicking on the appropriate module, selecting the forms needed and selecting print or review on screen. To save an SDG, choose from one of the following: • Save to New SDG B Append to Existing SDG The final folder is the Exception Reports. Here you can print an SDG specific Exception Report corit-uning the following information: Sample ID, Client ID, Exception Type, Parameter, QC Type, Result, Recovery, RPD, Low Limit High Limit and RPD Limit. Environmental Information Systems, Corporation Marrs QC Types SAM Sample MBΛV Method Blank Water MBS Method Blank Soil LCSW Laboratory Control Sample Water LCSWD Laboratory Control Sample Water Duplicate LCSS Laboratory Control Sample Solid LCSSD Laboratory Control Sample Solid Duplicate MS Matrix Spike MSD Matrix Spike Duplicate DUP Sample Duplicate SD Serial Dilution AS Post Digestion Spike ASD Post Digestion Spike Duplicate BS Blank Spike BSD Blank Spike Duplicate FB Fortified Blank DSH Laboratory Control Sample High DSL Laboratory Control Sample Low Instrument QC Types CAL Calibration Standard ICV Initial Calibration Verification ICB Initial Calibration Blank CCV Continuing Calibration Verification CCB Continuing Calibration Blank CRDL CRI/CRA Sample ICSA ICP Check Standard A ICSAB ICP Check Standard AB LRA Linear Range Standard LDS Low Digestion Standard MDS Mid Digestion Standard HDS High Digestion Standard PQL LOW PQL Low Environmental Information Systems, Corporation List Details A list of fields found in each list in the Associate List folder is provided below. Reporting List 1. Sequence 2. Cas Number 3. Parameter 4. Parameter Type 5. RDL (W) - Reporting Detection Limit for waters 6. RDL (S) - Reporting Detection Limit for solids 7. Report ? (Yes/No) 8. Parameter Initials (Element Symbol) 9. Report Method 10. Report Parameter (Element Name) 11. Wavelength 12. Background (AA and HG for form 10) 13. TCLP Regulatory Limits 14. STLC Regulatory Limits 15. Instrument units (W) - for waters 16. Instrument units (S) - for solids 17. Main Parameter QC Criteria List 1. Sequence 27. ICSA Criteria 2. Parameter 28. ICSAB Criteria 3. DDL - Instrument Detection Limit 29. PQL Low Criteria 4. MDLfW) - Method Detection Limit for Waters 30. I StcL Low 5. MDL(S) - Method Detection Limit for Solids 31. I Std. ffigh 6. LCSW Low 32. Blank Spike Low 7. LCSW High 33. Blank Spike High 8. LCSS Low (in mg/kg) 34. Blank Spike RPD 9. LCSS High (in mg/kg) 35. LDS Criteria 10. MS Low (W) 36. MDS Criteria 11. MS High (W) 37. HDS Criteria 12. MS Low (S) 38. Fortified Blank Criteria 13. MS High (S) 39. LDR Criteria 14. PDMS Low (Post Digest Spike) 40. Cal Criteria 15. PDMS High 41. LCSL Low Criteria 16. LCSWD RPD 42. LCSL High Criteria 17. LCSSD RPD 43. LCSH Low Criteria 18. MSD RPD (W) 44. LCSH High Criteria 19. MSD RPD (S) 45. ICB Multiplier Type 20. DUP RPD (W) 46. ICB Multiplier 21. DUP RPD (S) 47. CCB Multiplier Type 22. Serial Dilution Criteria 48. CCB Multiplier 23. PSMSD RPD 49. SD Multiplier Type (EX: X IDL) 24. ICV Criteria 50. SD Multiplier (EX: 50) 25. CCV Criteria 26. CRI/CRA Criteria Environmental Information Systems, Corporation True Values Lists - Enter and/or edit Standard Sources Per Instrument 1. Sequence 17. LCSL 2. Parameter 18. LCSH 3. LCSW 19. LDS 4. LCSS 20. MDS 5. MS fW) 21. HDS 6. MS (S) 22. ICV 7. PDMS 23. CCV 8. CRI/CRA 24. CalV 9. ICSA 25. Fortified Blank 10. ICSAB 11. PQL LOW 12. LRA TrueValue 13. Blank Spike 14. LDR 15. Integration Time 16. High Standard Review and Qualifier List Review Name All Samples (Yes/No) QC Type Parameter Type Sample Qualifier Global Qualifier Review Message (as seen on Exception Report) Review Group Review Type (Sample Level) Environmental Information Systems, Corporation Calculations Process List 1. Calculation Name 2. AH Samples (Yes/No) 3. QC Type 4. Parameter Type 5. Calc Group 6. Calc List Name 7. Calc Type (Sample Level) Significant Figures/Significant Digits Lists 1. Sequence 2. Parameter 3. Form 1 sig fig > = 100 (sig figs for results greater than or equal to 100 on form 1) 4. Form 1 sig dig >= 100 (sig digits for results greater than or equal to 100 on form 1) 5. Form 1 sig fig >= 10 6. Form 1 sig dig >= 10 7. Form 1 sig fig >= 1 8. Form 1 sig dig >= 1 9. Form 1 sig figs >= 0 10. form 1 sig dig >= 0 11. Form 2a sig dig for TrueValue 12. Form 2a sig figs Found Value 13. Form 2a sig dig Found Value 14. Form 2a sig dig Recovery 15. Form 2b sig dig for True Value 16. Form 2b sig figs Found Value 17. Form 2b sig dig Found Value 18. Form 2b sig dig Recovery 19. Form a si fi ICB/CCB 20. Form 3asi di ICB/CCB 21. Form 3a sig fig PB 22. Form 3a sig dig PB Environmental Information Systems, Corporation Significant Figures/Significant Digits List (Continued) 23. Form 4 sig dig True Value 36. Form 5b sig dig Recovery 24. Form 4 sig fig ICSA 37. Form 6 sig fig Result 25. Form 4 sig dig ICSA 38. Form 6 sig dig Result 26. Form 4 sig fig ICSAB 39. Form 6 sig dig RPD 27. Form 4 sig dig ICSAB 40. Form 7 sig dig True Value 28. Form 4 sig dig Recoveries 41. Form 7 sig fig Found Value 29. Form 5a sig fig Result 42. Form 7 sig dig Found Value 30. Form 5a sig dig Result 43. Form 7 sig dig Recovery 31. Form 5a sig dig Spike 44. Form 9 sig fig Result 32. Form 5a sig dig Recovery 45. Form 9 sig dig Result 33. Form 5b sig fig Result 46. Form 9 sig dig Percent D 34. Form 5b sig dig Result 47. Form 10 sig dig High Limit 35. Form 5b sig dig Spike 48. Form 10 sig dig Low Limit Print Set Up List 1. Form 1 to PQL (reports non-detect results to the PQL - flagged with a U and still reports trace values "B" between the 2. Form 3 to PQL reporting limit and the PQL) 3. Form 5a to PQL 4. Form 5b to PQL 5. Form 6 to PQL 6. Form 7 to PQL 7. Form 9 to PQL 8. Sig Dig for Formatting Percent Solids 9. Form 1 No B (reports all results below the PQL with a U - No Trace Values) 10. Form 3 No B

Claims: What is claimed is: 1. A computer-implemented analytical and reporting system for a test sample, the system comprising: input means operative for inputting analytical data results of the test sample; a database including an analysis methodology data section, an instrument data section and a forms data section, the analysis methodology data section including analysis methodology data for conducting at least one analysis method, the instrument data section including instrument data for modeling at least one analytical instrument, the forms data section including forms data for providing a desired one of a plurality of analytical report forms; and a processor operative for receiving, from the input means, the analytical data results of the test sample and receiving, from the database, the analysis methodology data of the at least one analysis method, the instrument data of at least one analytical instrument and the forms data of the desired analytical report form, for processing the analytical data results and instrument data using the analysis methodology data and for generating an analytical report produced on the desired one of the analytical report forms depicting final analytical results based on the at least one analysis method and the at least one analytical instrument.

Inventors: BANFER PAUL, BANFER, PAUL
Applicants: ENVIRONMENTAL INFORMATION SYST, ENVIRONMENTAL INFORMATION SYSTEMS, INC.
Application year: 2001
Main classification: G06F17
IPC codes: G01N35, G06F17, G06Q10