TEST REPORT: SIEVERS M-SERIES PERFORMANCE SPECIFICATIONS

Similar documents
The Sievers 900 Series TOC Analyzers

Sample Analysis Design Step 2 Calibration/Standard Preparation Choice of calibration method dependent upon several factors:

GUIDELINES FOR THE VALIDATION OF ANALYTICAL METHODS FOR ACTIVE CONSTITUENT, AGRICULTURAL AND VETERINARY CHEMICAL PRODUCTS.

Applying Statistics Recommended by Regulatory Documents

Analytical Test Method Validation Report Template

Step-by-Step Analytical Methods Validation and Protocol in the Quality System Compliance Industry

Validation and Calibration. Definitions and Terminology

To avoid potential inspection

USING CLSI GUIDELINES TO PERFORM METHOD EVALUATION STUDIES IN YOUR LABORATORY

ANALYTICAL METHODS INTERNATIONAL QUALITY SYSTEMS

A practical and novel standard addition strategy to screen. pharmacodynamic components in traditional Chinese medicine using

Develop a Quantitative Analytical Method for low (» 1 ppm) levels of Sulfate

Method Validation/Verification. CAP/CLIA regulated methods at Texas Department of State Health Services Laboratory

Analytical Methods: A Statistical Perspective on the ICH Q2A and Q2B Guidelines for Validation of Analytical Methods

International GMP Requirements for Quality Control Laboratories and Recomendations for Implementation

HPLC Analysis of Acetaminophen Tablets with Waters Alliance and Agilent Supplies

INTERNATIONAL JOURNAL OF PHARMACEUTICAL RESEARCH AND BIO-SCIENCE

Design of Experiments for Analytical Method Development and Validation

Definition of Minimum Performance Requirements for Analytical Methods of GMO Testing European Network of GMO Laboratories (ENGL)

Validating Methods using Waters Empower TM 2 Method. Validation. Manager

ASSURING THE QUALITY OF TEST RESULTS

Analytical Methods for Cleaning Validation

Online Total Organic Carbon (TOC)

VALIDATION OF ANALYTICAL PROCEDURES: TEXT AND METHODOLOGY Q2(R1)

KINETIC DETERMINATION OF SELENIUM BY VISIBLE SPECTROSCOPY (VERSION 1.8)

Implementing New USP Chapters for Analytical Method Validation

Evaluating Laboratory Data. Tom Frick Environmental Assessment Section Bureau of Laboratories

FOOD FOR THOUGHT Topical Insights from our Subject Matter Experts UNDERSTANDING WHAT IS NEEDED TO PRODUCE QUALITY DATA

ISO How to Meet. Requirements for Method Verification. Prepared by:

Methods verification. Transfer of validated methods into laboratories working routine. Dr. Manuela Schulze 1

QbD Approach to Assay Development and Method Validation

Assay Development and Method Validation Essentials

Ecology Quality Assurance Glossary

Guidance for Industry

ICH Topic Q 2 (R1) Validation of Analytical Procedures: Text and Methodology. Step 5

1 Quality Assurance and Quality Control Project Plan

Procedure for Writing Technical Procedures

Understanding Analytical Chemistry (Weighing, Mixing, Measuring and Evaluating)

How to Verify Performance Specifications

Quality Assurance/Quality Control in Acid Deposition Monitoring

4.2 Bias, Standards and Standardization

Magruder Statistics & Data Analysis

American Association for Laboratory Accreditation

1.0 XRF Analyses Performance Evaluation

Multi-elemental determination of gasoline using Agilent 5100 ICP-OES with oxygen injection and a temperature controlled spray chamber

Signal, Noise, and Detection Limits in Mass Spectrometry

OMCL Network of the Council of Europe QUALITY MANAGEMENT DOCUMENT

FT-NIR for Online Analysis in Polyol Production

Lifecycle Management of Analytical Procedures; What is it all about? Jane Weitzel Independent Consultant

Graphite Furnace AA, Page 1 DETERMINATION OF METALS IN FOOD SAMPLES BY GRAPHITE FURNACE ATOMIC ABSORPTION SPECTROSCOPY (VERSION 1.

Guide to Method Validation for Quantitative Analysis in Chemical Testing Laboratories

Proficiency testing schemes on determination of radioactivity in food and environmental samples organized by the NAEA, Poland

Using R for Linear Regression

Beräkningar enligt EN 14211, EN 14212, EN och EN

Qualification Study CHO 360-HCP ELISA (Type A to D)

Sample Analysis Design Isotope Dilution

Calibration Verification

USE OF REFERENCE MATERIALS IN THE LABORATORY

Analysis of Free Bromate Ions in Tap Water using an ACQUITY UPLC BEH Amide Column

DETERMINATION OF TOTAL CARBON, TOTAL ORGANIC CARBON AND INORGANIC CARBON IN SEDIMENTS

Measurement Systems Correlation MSC for Suppliers

Gas emission measurements with a FTIR gas analyzer - verification of the analysis method Kari Pieniniemi 1 * and Ulla Lassi 1, 2

Lead Testing and On Site Calibration for Water Testing Detection Range: 2 100ppb

Technical Guidance Manual for the Implementation of the Hawai`i State Contingency Plan. Interim Final SECTION 10

Calculating Nucleic Acid or Protein Concentration Using the GloMax Multi+ Microplate Instrument

Procedure for Equipment Calibration and Maintenance

Evaluation of Quantitative Data (errors/statistical analysis/propagation of error)

INTERNATIONAL OLIVE COUNCIL

Pearson's Correlation Tests

ANALYTICAL DETECTION LIMIT GUIDANCE. & Laboratory Guide for Determining Method Detection Limits

Reversed Phase High Presssure Liquid Chromatograhphic Technique for Determination of Sodium Alginate from Oral Suspension

Fairfield Public Schools

A Review of Statistical Outlier Methods

FP628. Nitrogen / Protein Determination by Combustion. Rev 1-6/8/11

Mass Spectrometry Signal Calibration for Protein Quantitation

THE LABORATORY NOTEBOOK

SPIKE RECOVERY AND DETERMINING A METHOD DETECTION LIMIT Pamela Doolittle, University of Wisconsin Madison, pssemrad@wisc.edu 2014

SOLUBILITY, IONIC STRENGTH AND ACTIVITY COEFFICIENTS

UNITED STATES CONSUMER PRODUCT SAFETY COMMISSION DIRECTORATE FOR LABORATORY SCIENCES DIVISION OF CHEMISTRY 5 RESEARCH PLACE ROCKVILLE, MD 20850

General and statistical principles for certification of RM ISO Guide 35 and Guide 34

Development of validated RP- HPLC method for estimation of rivaroxaban in pharmaceutical formulation

Environmental Water Testing: Surface Water, Groundwater, Hard Water, Wastewater, & Seawater

A Complete Solution for Method Linearity in HPLC and UHPLC

Assay Qualification Template for Host Cell Protein ELISA

TargetQuan 3 Software. Leading the way in regulatory. POPs quantification. Bullet Bullet Bullet

Spectrophotometer - Milton Roy Spectronic 21D or equivalent.

Project 5: Scoville Heat Value of Foods HPLC Analysis of Capsaicinoids

RARITAN VALLEY COMMUNITY COLLEGE ACADEMIC COURSE OUTLINE MATH 111H STATISTICS II HONORS

STANDARD OPERATING GUIDELINES: EVIDENTIAL BREATH ALCOHOL INSTRUMENT CALIBRATION

Content Sheet 7-1: Overview of Quality Control for Quantitative Tests

Spectrophotometry and the Beer-Lambert Law: An Important Analytical Technique in Chemistry

Quantifying measurement error from digital instruments

Methods of Dealing with Values Below the Limit of Detection using SAS

3.4 TEST FOR BACTERIAL ENDOTOXINS. Final text for revision of The International Pharmacopoeia

ACID-BASE TITRATIONS: DETERMINATION OF CARBONATE BY TITRATION WITH HYDROCHLORIC ACID BACKGROUND

The Fitness for Purpose of Analytical Methods

Determination of the Sensitivity Range of Biuret Test for Undergraduate Biochemistry Experiments

LAB ID and/or LABORATORY NAME: ASSESSOR NAME: CONTINUOUS RADON MONITOR (CRM) by Proportional Counting. Method Number: ELAP method code 7037

Experiment #1, Analyze Data using Excel, Calculator and Graphs.

Transcription:

TEST REPORT: SIEVERS M-SERIES PERFORMANCE SPECIFICATIONS. PURPOSE The purpose of this report is to verify the performance characteristics of the Sievers M-Series TOC Analyzers. Performance was quantified by measuring the accuracy, precision, linearity, limit of detection, and limit of quantification. The Sievers* M9 Analyzers used in this study included one laboratory, two portable, and five online Sievers M9 e units. 2. BACKGROUND INFORMATION AND CALCULATIONS 2. Accuracy The accuracy performance specification results are presented here as percent recoveries [,2]. The averages of replicates of sucrose standards were determined at the following concentrations: 25 ppb, 5 ppb, ppm, 5 ppm, ppm, 25 ppm, and 5 ppm. The percent recovery for each standard was calculated using the following equation: % Recovery = X % Percent recoveries close to % indicate a high degree of accuracy for the Analyzer. 2.2 Precision The precision performance specification data are presented as a % relative standard deviation (%RSD). The standard deviation of replicates and %RSD are calculated as follows: Standard Deviation: Where: x = Each result n = Number of measurements Relative Standard Deviation (%RSD) = X % A %RSD value close to % indicates a high degree of precision for the analyzer [-3].

2.3 System Suitability System suitability is a test commonly performed in the pharmaceutical industry to confirm the instrument s ability to recover both an easy and a difficult to oxidize compound [4,5]. A response efficiency of % indicates that the instrument recovered both compounds equally. Response Efficiency is calculated using the following equation: Response Efficiency = % Where Rss is the measured concentration of 5 ppb,4-benzoquinone (BQ), Rs is the measured concentration of 5 ppb sucrose, and Rw is the concentration of the reagent water blank. For USP/EP System Suitability, the acceptance criterion is a Response Efficiency between 85% and 5% [5]. 2.4 Limit of Detection/Limit of Quantification The limit of detection (LOD) is defined as the minimum concentration of TOC that can be reliably detected by the analyzer [,2]. It is calculated by the following: LOD = 3s Where: s = standard deviation of replicates of online DI water The limit of quantification (LOQ) is defined as the lowest concentration of TOC that can be determined quantitatively with an acceptable uncertainty [,2]. It is calculated via the equation: LOQ = s 2.5 Linearity Linearity is defined as the ability of the TOC analyzer to generate data that are directly proportional to the concentration of multiple TOC standards across the dynamic range of the instrument. Linearity is measured by calculating a correlation coefficient (R 2 ), slope of a regression line, and y-intercept. R 2 values close to. represent a high degree of correlation. 3. EXPERIMENTAL TEST PLAN 3. Sucrose and BQ Standards This study was divided into two separate parts in order to quantify performance specifications using various calibrations on three different instruments. One laboratory Sievers M9 unit and two portable Sievers M9 units were used in this study. Using the different calibrations, a wide range of sucrose standards were run to encompass the full 2

operating range of the analyzers and quantify differences (if any) between calibrations. Standard solutions of sucrose were produced at the following concentrations: 25 ppb, 5 ppb, ppb, 2 ppb, 25 ppb, 5 ppb, ppm, 5 ppm, ppm, 25 ppm, and 5 ppm. For accuracy and precision performance specifications, the standards in the concentration range of 25 ppb to 5 ppm were used. For linearity, all standards were used. To determine system suitability and response efficiency, 5 ppb BQ standards were analyzed. These BQ standards and the associated reagent water blanks were part of the System Suitability Standards Set made at GE Analytical Instruments. The table below outlines the order in which the samples were run on each instrument, the acid and oxidizer flow rates, and the number of repetitions. TOC concentration Testing for Acid (µl/min) Oxidizer (µl/min) Repetitions Reagent Water All.5 / 5 ppb Acc/Prec.5 / Rw for BQ System Suitability.5 / 5 ppb BQ System Suitability.5 / 25 ppb Linearity.5 / 5 ppb Linearity.5 / ppb Linearity.5 / 2 ppb Linearity.5 / 25 ppb Linearity/Acc/Prec.5 / 5 ppb Linearity/Acc/Prec.5 / ppm Linearity/Acc/Prec.. / 5 ppm Linearity/Acc/Prec..2 / ppm Linearity/Acc/Prec..6 / 25 ppm Linearity/Acc/Prec. 3.4 / 5 ppm Linearity/Acc/Prec. 6.8 / 3.2 All Analyzers with ppm The three analyzers were each calibrated using a ppm single-point calibration using KHP and Na 2 CO 3 as outlined in GE protocols [6]. Once the analyzers were calibrated at ppm and verified at 5 ppb, all of the sucrose and BQ standards were analyzed as described above. 3.3 Analyzers with Three Different s After the completion of all samples using the ppm calibration, the three analyzers were recalibrated as follows: Lab 39: Multi-Point (25 ppb, ppm, 5 ppm, ppm, 25 ppm, 5 ppm TOC as KHP, and ppm IC as Na 2 CO 3 ) Portable 42: 5 ppm Single-Point Portable 43: ppm Single-Point New aliquots of the same sucrose and BQ standards were then run on each instrument with these new calibrations. 3

4. TEST EQUIPMENT USED Sievers M9 Laboratory TOC Analyzer Serial Number: 32 39 Sievers M9 Portable TOC Analyzer Serial Number: 442 Sievers M9 Portable TOC Analyzer Serial Number: 443 GE Autosampler Serial Number: 424 GE Autosampler Serial Number: 323 GE Autosampler Serial Number: 945 DataPro2 Software 5. CALIBRATION AND VERIFICATION Please refer to sections 3.2 and 3.3. 6. RESULTS AND DISCUSSION All results presented here are for replicates of each sucrose standard (25 ppb-5 ppm) with no rejects. There was one statistical outlier on the 25 ppm sucrose standard on Lab 39 using the ppm calibration, which was determined using a Grubb s statistical test for outliers [-3] at the 99% confidence level. This data point was discarded. 6. Precision Lab 39 ppm Cal 25 ppb 2.2 ppb.9% ppm Cal 5 ppb 2.7 ppb.5% ppm Cal ppm 6.7 ppb.6 % ppm Cal 5 ppm 9.3 ppb.4 % ppm Cal ppm 78.9 ppb.8 % ppm Cal 25 ppm 22 ppb.5 % ppm Cal 5 ppm 362 ppb.7 % Multi-Point Cal 25 ppb.9 ppb.8% Multi-Point Cal 5 ppb 3.3 ppb.7 % Multi-Point Cal ppm 4.8 ppb.5 % Multi-Point Cal 5 ppm 5.2 ppb.3% Multi-Point Cal ppm 7 ppb.7% Multi-Point Cal 25 ppm 5 ppb.6 % Multi-Point Cal 5 ppm 36 ppb.7 % Portable 42 ppm Cal 25 ppb 2. ppb.8 % ppm Cal 5 ppb 3.9 ppb.8 % ppm Cal ppm 9.5 ppb.9 % 4

ppm Cal 5 ppm 8.4 ppb.4 % ppm Cal ppm 48.3 ppb.5 % ppm Cal 25 ppm 9.9 ppb.4 % ppm Cal 5 ppm 399 ppb.8 % 5 ppm Cal 25 ppb 4.7 ppb.% 5 ppm Cal 5 ppb 4. ppb.7% 5 ppm Cal ppm 7.4 ppb.7 % 5 ppm Cal 5 ppm 9. ppb.4 % 5 ppm Cal ppm 42.2 ppb.4 % 5 ppm Cal 25 ppm 67.5 ppb.3 % 5 ppm Cal 5 ppm 323 ppb.6 % Portable 43 ppm Cal 25 ppb 2. ppb.8 % ppm Cal 5 ppb 2.3 ppb.4% ppm Cal ppm 6.7 ppb.6 % ppm Cal 5 ppm 3.3 ppb.6 % ppm Cal ppm 63.2 ppb.6 % ppm Cal 25 ppm 7 ppb.3 % ppm Cal 5 ppm 27 ppb.5 % ppm Cal 25 ppb.8 ppb.7% ppm Cal 5 ppb 2.3 ppb.4% ppm Cal ppm 8.4 ppb.8% ppm Cal 5 ppm 2.2 ppb.4% ppm Cal ppm 85. ppb.8% ppm Cal 25 ppm 78.9 ppb.3% ppm Cal 5 ppm 272 ppb.6% 6..2 Precision Statistics Using a two-tailed Student s t-test, it was assessed whether or not instrument precision (as %RSD) was statistically different depending on the calibration or depending on the individual unit [,2]. At the 99% confidence level, there is no statistical difference (p>.) between the precision of the instruments regardless of calibration nor was there a statistically significant difference between the precision of each individual analyzer. The following table outlines the p-value results of the Student s t-tests for the precision of each analyzer. Instrument Average %RSD ppm Cal Standard Deviation Average %RSD Alternate Cal Lab 39.62%.7%.6% (Multi-Point cal) Portable 42.64%.23%.6% (5 ppm cal) Standard Deviation p-value (Student s t-test).6%.85.25%.62 5

Portable 43.57%.5%.58% ( ppm cal) All Units.6%.8%.58% (all alternate cals).2%.95.2%.68 6..3 Precision Performance Specification Based on the data reported here, the precision performance specification for the Sievers M-Series TOC Analyzers is %. 6.2 Accuracy 6.2. Percent Recoveries TOC Concentration %Recovery Lab 39 ppm % Recovery Lab 39 Multi-Point 6.2.2 Accuracy Performance Specification % Recovery Portable 42 ppm % Recovery Portable 42 5 ppm % Recovery Portable 43 ppm % Recovery Portable 43 ppm 25 ppb 98.6% 98.%.% 4.7% 99.% 99.6% 5 ppb 99.3% 97.8% 99.5% 4.2% 99.5% 99.4% ppm.9% 99.5% 99.6% 4.6%.4%.8% 5 ppm.6% 99.9% 99.% 3.7%.5%.4% ppm 2.% 99.2% 99.2% 3.%.2% 99.2% 25 ppm.7% 98.8% 96.5%.6% 98.5% 98.5% 5 ppm 99.5% 97.% 95.4%.% 96.9% 96.4% The results presented here demonstrate a high degree of accuracy of the Sievers M9 Analyzers regardless of the calibration. Several recommendations on the optimal calibration for particular sample concentrations include the following: ) The ppm calibration produced recoveries of 98.6% to.9% on all three instruments in the 25 ppb to 5 ppm range. On two of the instruments, using the ppm calibration produced recoveries of 99.2% and.2% at the ppm concentration indicating that using this calibration is still sufficient even at concentrations times higher than the single calibration point. 2) The Multi-Point provided excellent results (98.8% to 99.5%) in the ppm to 25 ppm TOC concentration range. Customers regularly running samples in this range can use this type of calibration if desired, though a single-point ppm calibration produces equivalent recoveries. Below ppm and above 25 ppm, the recoveries were lower by 2.% to 2.9% using the multi-point calibration. 3) The 5 ppm single-point calibration provided the best results only at 5 ppm. A slightly lower calibration slope was likely produced using this type of calibration than the other calibration types leading to higher percent recoveries on all of the lower TOC concentrations (.6% to 4.7%). 4) The ppm calibration had excellent recoveries (98.5% to.8%) in the range of 25 ppb to 25 ppm. Recovery was slightly lower (96.4%) at 5 ppm, but that TOC concentration was five times higher than the single calibration point, so the results are not unexpected. On Portable 43 the unit that had both the ppm and the ppm calibrations there was no 6

statistical difference between the percent recoveries using either calibration in the 25 ppb to 5 ppm range (p>.). 5) As a general guideline, measurements on the Sievers M9 Analyzers should be either at or below the calibration point. Based on the recoveries discussed above, the accuracy performance specification of the Sievers M-Series TOC Analyzers are ±2% when using the appropriate calibration based on the TOC range of the samples. 6.3 Linearity To demonstrate linearity, least-squares regression lines for a wide range of TOC concentrations were plotted (25 ppb to 5 ppm). Results of these regressions as well as the correlation coefficients (R 2 ) are reported in this section of the results. These results are separated into two subsections with one demonstrating linearity of the full instrument range (up to 5 ppm) and the other showing linearity of the instrument across lower TOC concentrations (25 ppb ppm). Each of these subsections includes linearity plots for the different calibrations on each instrument. 6.3. Linearity Across the Full Instrument Range (up to 5 ppm) 6 5 4 3 2 Lab 39 ppm y =.9967x +.396 R² =. 2 4 6 6 5 4 3 2 Lab 39 Multi-Point y =.974x +.523 R² =.9999 2 4 6 6 5 4 3 2 Portable 42 ppm y =.9555x +.738 R² =.9999 6 5 4 3 2 Portable 42 5 ppm y =.28x +.72 R² =.9999 2 4 6 2 4 6 7

6 5 4 3 2 Portable 43 ppm y =.977x +.672 R² =.9999 6 5 4 3 2 Portable 43 ppm y =.9668x +.744 R² =.9999 2 4 6 2 4 6 6.3.2 Linearity Across Low TOC Concentrations (up to ppm).2.8.6.4.2 Lab 39 ppm y =.2x -.57 R² =.9999.2.8.6.4.2 Lab 39 Multi-Point y =.995x -.29 R² =.9999..2.4.6.8..2.2.8.6.4.2 Portable 42 ppm y =.9957x +. R² =...2.4.6.8..2.2 Portable 43 ppm.8.6.4.2 y =.67x -.4 R² =...2.4.6.8..2..2.4.6.8..2.2.8.6.4.2 Portable 42 5 ppm y =.45x +. R² =...2.4.6.8..2.2 Portable 43 ppm.8.6.4.2 y =.94x -.35 R² =...2.4.6.8..2 8

6.3.3 Linearity Performance Specification All three instruments demonstrated highly linear responses (R 2.9999) across the full range of the instrument as well as at low TOC levels with the four different calibration options. 6.4 System Suitability Instrument Response Efficiency Lab 39 ppm.9% Lab 39 Multi-Point 99.7% Portable 42 ppm.2% Portable 42 5 ppm 99.6% Portable 43 ppm.6% Portable 43 ppm 99.3 % System suitability results from this experiment (99.3% to.9% response efficiency) demonstrate the excellent response efficiency of the Sievers M9 Analyzers for all calibration types. These response efficiencies are well within the acceptable USP/EP System Suitability range of 85% to 5% [5]. 6.5 LOD/LOQ To determine the LOD and LOQ of the Sievers M-Series Analyzers, replicates of DI water on five Sievers M9 e On-Line units were used. These units had serial numbers: 5, 5, 52, 54, and 59. In order to eliminate variability in TOC measurements due to water system changes, the Sievers M9 e units were run for 24 hours. The replicates for the LOD and LOQ calculations were selected during the most stable hour-long time span of the water system. The table below outlines the standard deviation for these reps on each instrument, the average standard deviation, as well as the LOD and LOQ. SIEVERS M9e Serial Number Standard deviation ( reps) 5.3 5. 52.2 54.9 59.8 Average.84 LOD.3 LOQ.8 Based on the standard deviations of ten replicates for each of these units, the LOD and LOQ for the Sievers M-Series Analyzers are: LOD =.3 ppb and LOQ =.8 ppb 9

7. CONCLUSIONS In summary, the performance specifications for the Sievers M-Series TOC Analyzers have been experimentally verified as follows: Accuracy ±2% (25 ppb to 5 ppm) Precision Linearity LOD LOQ % (25 ppb to 5 ppm) R 2.9999 (25 ppb to 5 ppm).3 ppb.8 ppb 8. REFERENCES. Barwick, V., S. Burke, R. Lawn, P. Roper, and R. Walker. (2). Applications of Reference Materials in Analytical Chemistry. Cambridge: LGC Limited. 2. Ellison, S.R., V.J. Barwick, and T.J. Duguid Farrant. (29). Practical Statistics for the Analytical Scientist. Cambridge: RSC Publishing. 3. Taylor, J.K. (987). Quality Assurance of Chemical Measurements. Florida: CRC Press LLC. 4. ICH Harmonized Tripartite Guideline Validation of Analytical Procedures: Text and Methodology Q2(R). (25). 5. USP <643> Total Organic Carbon. 6. Sievers M9/M9 e TOC Analyzers Operation and Maintenance Manual..4Rev Firmware. DLM 77- EN Rev D. * Trademark of General Electric Company; may be registered in one or more countries. The Americas GE Analytical Instruments 66 Spine Road Boulder, CO 83-3687 USA T + 8 255 6964 T + 33 444 29 F + 33 527 797 geai@ge.com Europe/Middle East/Africa GE Analytical Instruments Unit 3, Mercury Way Urmston, Manchester UK M4 7LY T +44 () 6 864 68 F +44 () 6 864 6829 geai.europe@ge.com Asia Pacific GE Analytical Instruments 7/F, Building, No. Hua Tuo Rd, ZhangJiang Hi-Tech Park,, Pudong Shanghai, China 223 T + (862) 38777735 F + (862) 38777469 geai.asia@ge.com 25, General Electric Company. All rights reserved. MC5-6 3 29 Rev. B