A Discussion of Measurement of Uncertainty for Life Science Laboratories

Similar documents
Estimating MU for microbiological plate count using intermediate reproducibility duplicates method

GOODSamples: Guidance for Obtaining Defensible Samples

Analytical Measurement Uncertainty APHL Quality Management System (QMS) Competency Guidelines

This procedure describes the monitoring activities in a laboratory quality control (QC) program to ensure the quality of test results.

I used college textbooks because they were the only resource available to evaluate measurement uncertainty calculations.

Sources of variability in measuring aflatoxin and the role of sampling

APPENDIX G EVALUATION OF MEASUREMENT UNCERTAINTY

Validation and Standardization of (Bio)Analytical Methods

3.1.1 The method can detect, identify, and potentially measure the amount of (quantify) an analyte(s):

serve the goal of analytical lmethod Its data reveals the quality, reliability and consistency of

Precision estimated by series of analysis ISO and Approach Duplicate Approach

Measurement Uncertainty

Analytical Measurement Uncertainty

APPENDIX G ESTIMATION OF UNCERTAINTY OF MEASUREMENT

Journal of Consumer Protection and Food Safety Journal für Verbraucherschutz und Lebensmittelsicherheit

Laboratory Techniques 100: Back To Basics. Carol Injasoulian Lab Manager City of Bay City April 29,2015

Protocol for the design, conducts and interpretation of collaborative studies (Resolution Oeno 6/2000)

Schedule. Draft Section of Lab Report Monday 6pm (Jan 27) Summary of Paper 2 Monday 2pm (Feb 3)

And how to do them. Denise L Seman City of Youngstown

NATIONAL ASSOCIATION OF TESTING AUTHORITIES (NATA) REQUIREMENTS FOR ACCREDITATION OF ICP-MS TECHNIQUES

University of Tennessee Safety Procedure

COURSE SYLLABUS (Formally the CIS)

Standard Operating Procedure for the Analysis of Dissolved Inorganic Carbon CCAL 21A.1

OF ANALYSIS FOR DETERMINATION OF PESTICIDES RESIDUES IN FOOD (CX/PR 15/47/10) European Union Competence European Union Vote

Hach Method Total Organic Carbon in Finished Drinking Water by Catalyzed Ozone Hydroxyl Radical Oxidation Infrared Analysis

EPA's Revision to the 40 CFR Part 136 Method Detection Limit (MDL) Procedure

EPAs New MDL Procedure What it Means, Why it Works, and How to Comply

Convenor: Colin Fricker Co-convenor: Olivier Molinier Objective of the revisionof ISO 13843

Aflatoxin M1 (AFM1) ELISA Kit

The New MDL Procedure How To s. Presented by: Marcy Bolek - Alloway

Method Validation and Accreditation

Copyright ENCO Laboratories, Inc. II. Quality Control. A. Introduction

Part 14: Water quality Sampling. Guidance on quality assurance and quality control of environmental water sampling and handling

RADIATION SAFETY GUIDELINES FOR NON-USERS

SWGDRUG GLOSSARY. Independent science-based organization that has the authority to grant

Hach Method Spectrophotometric Measurement of Free Chlorine (Cl 2 ) in Finished Drinking Water

VAM Project Development and Harmonisation of Measurement Uncertainty Principles

ALLOWAY METHOD OUTLINE

BIOO FOOD AND FEED SAFETY. Histamine Enzymatic Assay Kit Manual. Catalog #: Reference #:

Statistics for Engineering, 4C3/6C3 Written midterm, 16 February 2012

Uncertainty of Measurement (Analytical) Maré Linsky 14 October 2015

Certificate of Analysis

A Laboratory Guide to Method Validation, (Eurachem).

Document No: TR 12 Issue No: 1

1.11 Measurement Uncertainty

Anand pointed out that the adjournment time in Section 6 should be EDT.

Certificate of Analysis

Signal, Noise, and Detection Limits in Mass Spectrometry

This document is meant purely as a documentation tool and the institutions do not assume any liability for its contents

Draft Guideline on Bioanalytical Method Validation in. Pharmaceutical Development. (15 April 2013, MHLW, Japan)

Strands & Standards MEDICAL MATH

EXAMINATIONS OF THE ROYAL STATISTICAL SOCIETY

CCME Reference Method for the Canada-Wide Standard for Petroleum Hydrocarbons (PHC) in Soil - Tier 1 Method

Topic 2 Measurement and Calculations in Chemistry

Use of the 3M Molecular Detection System for Salmonella and Listeria spp.

Glossary of Common Laboratory Terms

DECISION LIMITS FOR THE CONFIRMATORY QUANTIFICATION OF THRESHOLD SUBSTANCES

The Role of Proficiency Tests in the Estimation of Measurement Uncertainty of PCDD/PCDF and PCB Determination by Isotope Dilution Methods

How s that *new* LOD Coming? Rick Mealy WWOA Board of Directors DNR LabCert

Oddo-Harkins rule of element abundances

MEASUREMENT VARIATION

Sýnishorn. Water quality Enumeration of Clostridium perfringens Method using membrane filtration

Results of the EPA Method 1631 Validation Study

NOTICE: This method: The laboratories have to study the instrumental conditions appropriate for their own instrumentation.

Proposed Procedures for Determining the Method Detection Limit and Minimum Level

Standard Operating Procedure for: ph using Oakton ph 5+ Handheld ph Meter. Missouri State University. and

Chapter 8: Sampling, Standardization, and Calibration

Laboratory ID. Laboratory Name. Analyst(s) Auditor. Date(s) of Audit. Type of Audit Initial Biennial Special ELCP TNI/NELAP.

ESTIMATION OF ANALYTICAL METHOD DETECTION LIMITS (MDL)

Direct Determination of Cadmium and Lead in honey by Electrothermal Atomization Atomic Absorption Spectrometry with Zeeman Effect Correction

Draft Guideline on Bioanalytical Method (Ligand Binding Assay) Validation in Pharmaceutical Development. (24 January, 2014, MHLW, Japan)

Deoxynivalenol, sometimes called DON or vomitoxin,

LAP-013. Procedure Title: Date: 6/28/96. Author: Raymond Ruiz and Tina Ehrman ISSUE DATE: 8/26/96 SUPERSEDES: 11/01/94.

Measurement Uncertainty: A practical guide to understanding what your results really mean.

Best Practices for Obtaining Samples of Known Quality

DEPARTMENT OF ANIMAL HEALTH TECHNOLOGY COURSE OUTLINE - FALL 2014 LAB PROCEDURES AND MICROBIOLOGY AH 174 E- MAIL:

QUALITY ASSURANCE AND QUALITY CONTROL IN CHEMICAL AND PHYSICAL ANALYSIS

Specific Accreditation Guidance. Infrastructure and Asset Integrity. Measurement Uncertainty in Geotechnical Testing

Measurement Uncertainty Principles and Implementation in QC

ISO/TS TECHNICAL SPECIFICATION. Water quality Guidance on analytical quality control for chemical and physicochemical water analysis

REX Evaluation Guide. American Micro Detection Systems Inc March Lane, Suite 200 Stockton, CA 95219

Analytical Performance & Method. Validation

Direct Determination of Aluminium in Milk by Graphite Furnace Atomic Absorption Spectrometry

The Comprehensive Report

STP-TS THERMOPHYSICAL PROPERTIES OF WORKING GASES USED IN WORKING GAS TURBINE APPLICATIONS

MEASUREMENT UNCERTAINTY PREPARED FOR ENAO ASSESSOR CALIBRATION COURSE OCTOBER/NOVEMBER Prepared by MJ Mc Nerney for ENAO Assessor Calibration

Chemical Engineering: 4C3/6C3 Statistics for Engineering McMaster University: Final examination

What is measurement uncertainty?

PROJECT ID: W09341 LABORATORY REPORT NUMBER: L

The lightning phenomenon eventually brought to you

Determination of particle size distribution Single particle light interaction methods. Part 4:

Proportional Relationships

Application of Detection and Quantification Concepts to Chlorine Residual Measurements

Using cold vapor generation atomic absorption to determine mercury impurities in pharmaceutical products

How to do a Gage R&R when you can t do a Gage R&R

3590/ Laboratory

Prerequisite: CHEM 1311 General Chemistry I (lecture) and CHEM 1111 General Chemistry I Laboratory or CHEM 1411.

Certificate of Analysis

STUDENT INFORMATION PLAN (SIP) DEVELOPMENTAL MATHEMATICS MATH 0310 BEGINNING ALGEBRA - TDCJ

EFFECT OF THE UNCERTAINTY OF THE STABILITY DATA ON THE SHELF LIFE ESTIMATION OF PHARMACEUTICAL PRODUCTS

Transcription:

Webinar A Discussion of Measurement of Uncertainty for Life Science Laboratories 12/3/2015 Speakers Roger M. Brauninger, Biosafety Program Manager, A2LA (American Association for Laboratory Accreditation), Frederick, Maryland Roger M. Brauninger, Biosafety Program Manager has been employed with the American Association for Laboratory Accreditation since February 1999. He provides assistance in the day-to-day laboratory accreditation operations for laboratories in the Environmental, Biological, and Chemical fields and Reference Material Producers and serves as staff contact to organizations dealing with food and drug safety, biodefense and threat monitoring in the Biological and Chemical fields. Objectives At the conclusion of this program, participants will be able to: Identify the types of analytical methods which require an estimate of measurement uncertainty Discuss ways the laboratory can use commonly collected laboratory data to calculate an acceptable estimate of uncertainty and when it needs to be recalculated Continuing Education Credit CE credit is not available for this program, but you will receive a Certificate of Attendance. Evaluation/Certificate of Attendance Process Continuing education credit is not available for this program. Individuals who successfully complete the program and evaluation by 10/20/2016 will receive a Certificate of Attendance. Go to https://www.surveymonkey.com/r/100-0:00-15jr to complete the evaluation. 1. After you complete the evaluation, you will automatically receive the Certificate of Attendance. 2. Type or print your name on the certificate. Archived Program The archived streaming video will be available within two days. Anyone from your site can register view the program. URL: http://eventcenter.commpartners.com/se/meetings/playback.aspx?meeting.id=598436 Comments, opinions, and evaluations expressed in this program do not constitute endorsement by APHL. The APHL does not authorize any program faculty to express personal opinion or evaluation as the position of APHL. The use of trade names and commercial sources is for identification only and does not imply endorsement by the program sponsors. This program is copyright protected by the speaker(s) and APHL. The material is to be used for this APHL program only. It is strictly forbidden to record the program or use any part of the material without permission from the author or APHL. Any unauthorized use of the written material or broadcasting, public performance, copying or re-recording constitutes an infringement of copyright laws. ACKNOWLEDGEMENT These webinars are supported by a Cooperative Agreement funded by FDA, through which APHL, AFDO and AAFCO are working to build an Integrated Laboratory System to Advance the Safety of Food and Animal Feed. For more information about ISO/IEC 17025 Accreditation go to: http://www.aphl.org/aphlprograms/food/laboratory-accrediation/pages/default.aspx This project was 100% funded with federal funds from a federal program of $1,100,000. The Association of Public Health Laboratories (APHL) sponsors educational programs on critical issues in laboratory science. For more information, visit www.aphl.org/courses

Simple Measurement Uncertainty: Roger Brauninger American Association for Laboratory Accreditation Frederick, Maryland Topics Why do we need to determine MU? When do we need to recalculate? How large is too large? How do we calculate MU? RSS LCS Replicates and MPN 2 Measurement uncertainty Helps determine the quality of the testing. Measurable basis to determine improvements. Estimates variability of testing over time: materials, equipment, environment, and people; Tells the range of values that are about equally likely to appear as the result of the same measurement procedure on a particular sample. 3 1

ISO/IEC 17025 5.4.6.2 Testing laboratories shall have and shall apply procedures for estimating uncertainty of measurement. Reasonable estimation shall be based on knowledge of the performance of the method and Shall make use of, for example, previous experience and validation data. 4 A Few Terms Variance: Average of the squared differences from the Mean. Standard Deviation (SD): Square root of the Variance. Relative Standard Deviation (RSD): SD divided by the Mean x 100) Standard Uncertainty (u): Total of the combined uncertainty contributors (or the single contributor, if there is only one component). Expanded Uncertainty (U): Combined uncertainty contributors (or the single contributor, if there is only one component), multiplied by the coverage factor (k) @ 95% confidence interval, assuming normal distribution. 5 Students t test coverage factor (k)= 6 2

Measurement uncertainty s Essence: There are two major factors to consider Repeatability describes the variability of results when doing the testing sequentially; time after time under the same conditions. Reproducibility describes the variability across different testing conditions; changes in time, personnel, environment, and equipment. Both must be considered to get accurate picture of process variability. 7 Sources of Measurement Uncertainty: Variation in method performance Different analysts Sampling effects Different weighing/pipetting techniques Differences in platting techniques Background Effects 8 Sources of Measurement Uncertainty: of microbiological test methods? Variation in controls/rm Storage Conditions Sample or Matrix Effects Living positive/process control Unable to count the CFU directly Unable to determine viable CFU directly Different sources of CRMs/RMs Purity differences Uncertainties differ 9 3

Sources of Measurement Uncertainty: Variation in media/reagents/equipment Each batch of media prepared Different technician, Different lot # of media, Different autoclave cycle Each reagent solution preparation Reagent Purity Variation in equipment Sensitivity LOD Detectors 10 Sources of Measurement Uncertainty of microbiological test methods? Variation in incubation conditions Method allows range in incubation time Method allows range in incubation temperature Extractions times, solvents, temps, matrices Organisms are unpredictable! 11 When to Consider Recalculating MU? When something in the process changes New analyst(s) New equipment New method for testing or for preparing control New Reagents/ Positive controls Annually? 12 4

How large an MU estimate is too large? Ask yourself if it is Acceptable to the lab if need to report? Acceptable to the customer/regulator if need to report? Reflective of laboratory capability? 13 A few Measurement uncertainty estimation variations. Root Sum Squared Method LCS (e.g., SD x k )Method Using Data Generated From Replicates and Most Probable Number (MPN) Method 14 Root Sum Squared Method 15 5

Root Sum Squared Method: Microbiology Lab Control data: SD[or RSD*] x k Methods Values obtained for RSS must be in the same unit The formula requires the data to be linear. But microbiological data is logarithmic Therefore MUST convert to base 10 (or natural base) ` *NOTE: Because it is not relative to the concentration of the sample, when using SD of data sets, the uncertainty value is added/ subtracted., thus it would be the same across all concentrations for that method. When using RSD of data sets, the uncertainty value is multiplied, as the value is being compared and is relative to the data produced. 16 Root Sum Squared Method A Hypothetical Example: a = uncertainty due to analyst (5%) b = uncertainty due to equipment (1%) c = uncertainty due to media prep (4%) n = the rest (<1%) 17 Hypothetical example using Root Sum Squared Method Root Sum Squared Method Bottoms Up approach Must Identify all contributors Must assign a value u = 18 6

Hypothetical example using Root Sum Squared Method u = (0.05) 2 + (0.01) 2 + (0.04) 2 + (0.01) 2 u = 0.0025 + 0.0001 + 0.0016 + 0.0001 u = 0.066 Ue = 2 x 0.066 = 0.132 = 13.2% 19 e.g., count of 120 CFU Step 1 Transform the CFU value to log 10 value. (e.g., 120 CFU = 2.0792 (log 10 )) Step 2 Calculate the SD of the log 10 values. SD= 0.066. Step 3 Apply the coverage factor (95%, k=2) to the SD to obtain the relative Ue. (e.g., rue = 0.0.132 or 13.2%). Step 4 The log value is multiplied by rue (e.g., Ue= 2.0792 x 0.132 = 0.2724) Step 5 The Ue is added and subtracted from the log value. (e.g., (2.0792 0.2724) = 1.8068 and (2.0792 + 0.2724) = 2.3516 Step 6 - Convert the log value for the sample measurement back to CFU for the reported result. This is accomplished by taking the anti-log of each of the endpoints of the interval (anti-log of x = 10 x ). (e.g., 10 1.8068 = 64.1 = 64 CFU and 10 2.3516 = 224.7 = 225 CFU) Uncertainty interval = 64 225 CFU 20 LCS Data (e.g., SD x k Method) 21 7

Chemical: Aflatoxin example Values of method from the spiked recoveries of the aflatoxin results were plotted on control charts and the standard deviations then determined Alfatoxin (ppb) Statistics Sample 1 10 Mean 11.11538 2 12 SD 1.142871 3 10 RSD 10.08222 4 10 MU (SD x k) 2.285742 5 10 MU (RSD x k) 20.56377% 6 10 7 10 8 10 9 10 10 10 11 10 12 12 13 12 14 10 15 10 16 12 17 12 18 12 19 12 20 12 21 13 22 13 23 11 24 11 25 12 26 13 22 Laboratory Control Data with Same Target Value (e.g., 100 CFU) Raw Data (actual CFU Log 10 Value Difference from Mean Difference Squared recovered) (Log 10 Value) VAR=0.1121 X= 1.8860 SD= 0.3348 131 2.1173 0.2313 0.0535 69 1.8388-0.0472 0.0022 45 1.6532-0.2328 0.0542 40 1.6021-0.2839 0.0806 31 1.4914-0.3946 0.1557 33 1.5185-0.3675 0.1351 31 1.4914-0.3946 0.1557 37 1.5682-0.3178 0.1010 186 2.2695 0.3835 0.1471 218 2.3385 0.4525 0.2048 200 2.3010 0.415 0.1722 39 1.5911-0.2949 0.0870 217 2.3365 0.4505 0.2030 119 2.0755 0.1895 0.0359 28 1.4472-0.4388 0.1925 106 2.0253 0.1393 0.0194 107 2.0294 0.1434 0.0206 45 1.6532-0.2328 0.0542 98 1.9912 0.1052 0.0111 240 2.3802 0.4942 0.2442 23 Microbial Laboratory Control Data Using the Standard Deviation (SD) Step 1 Transform the CFU values to log 10 value. Step 2 Calculate the SD of the log 10 values. SD= 0.3348. Step 3 Apply the coverage factor (95%, k=2) to the SD to obtain Ue. The Ue in this example is 0.6696. If using the student t-tables, with n=20 (19 degrees of freedom), the coverage factor k would be 2.09, which would provide an expanded uncertainty of 0.6998. 24 8

Microbial Laboratory Control Data Using the Standard Deviation Step 4 To calculate the uncertainty for any subsequent laboratory result using SD x k, the result is first converted to log base 10 value (log 10 ), and the expanded uncertainty of 0.6696 is added and subtracted from the log value. Step 5 - Convert the log value for the sample measurement back to CFU for the reported result. This is accomplished by taking the anti-log of each of the endpoints of the interval (anti-log of x = 10 x ). For example, estimating the uncertainty using SD x k for a result of 150 CFU: 150 in log 10 = 2.1761. Adding and subtracting 0.6696 from 2.1761 gives an interval from 1.5065 to 2.8457; transforming back to counts: 10 1.5065 =32.10, and 10 2.8457 =700.97. Therefore the uncertainty interval is 32 to 701 CFU. 25 Microbial Laboratory Control Data Using the Relative Standard Deviation Step 1 Transform the CFU values to log 10. Step 2 Calculate the mean and relative standard deviation (RSD) of the log 10 values. The percentage SD (or relative SD), in log units: 0.3348/1.8860 = 0.1775, or 17.8%; Step 3 Apply the coverage factor to the RSD to obtain the relative expanded uncertainty. For 95% coverage we use a coverage factor of k=2. The relative expanded uncertainty is thus 2 x 0.1775=0.3550, or 35.5%. Note: If using the student t-tables, with n=20 (19 degrees of freedom), the coverage factor k would be 2.09, which would provide an relative expanded uncertainty of 0.3710 or 37.10%. 26 Microbial Laboratory Control Data Using the Relative Standard Deviation Step 4 To estimate MU for any subsequent laboratory result using RSD x k: The result is first converted to the log 10 value, Multiplied by 0.355 (35.5% converted to decimal) and The expanded uncertainty is added and subtracted from the log value. Step 5 To obtain CFU for the reported result Convert the log value for the sample measurement back. by taking the anti-log of each of the endpoints of the interval (anti-log of x = 10 x ). 27 9

Microbial Laboratory Control Data Using the Relative Standard Deviation For estimating MU using RSD x k for a result of 150 CFU: 150 in log 10 = 2.1761 and the relative expanded uncertainty in log counts is 2.1761 x 0.355 = 0.7725. Add and subtract from 2.1761 gives an interval from 1.4036 to 2.9486; Transform back to counts: 10 1.4036 =25.33, and 10 2.9486 = 888.41. Therefore the uncertainty interval is 25 to 889 CFU. NOTE: UM can also remain as a % and the lab can express upper and lower control limits as the mean (in CFU) ± 3 x RSD. 28 Microbial Replicates But Not all are the same 29 Sources of uncertainty reflected in different types of replicates Type of Replicate Source Reproducibility Recovery True Plate Random error X X X X Counting error X X X X Dilutions X X X Environment X X Equipment X X Analyst X X 30 10

Reproducibility Replicates Results derived from laboratory control samples, not test samples. Sources of uncertainty are reflected in the differences between replicates. The difference between each pair of log counts is converted into a variance (squared difference). These variances are pooled and converted into an estimate of the combined standard uncertainty. 31 Reproducibility Replicates Raw Data Log 10 Raw Data (actual Log 10 Difference between Difference (actual CFU Value CFU recovered) Value Replicates between recovered) Second Replicate X=1.9219 (Log 10 Value) Replicates First Replicate Squared VAR=0.00919 SD=0.0959 Column 1 Column 2 Column 3 Column 4 Column 5 Column 6 131 2.1173 142 2.1523-0.0350 0.00123 69 1.8388 90 1.9542-0.1154 0.01332 45 1.6532 76 1.8808-0.2276 0.05180 40 1.6021 55 1.7404-01383 0.01913 31 1.4914 20 1.3010 0.1903 0.03623 33 1.5185 40 1.6021-0.0835 0.00698 31 1.4914 62 1.7924-0.3010 0.09062 37 1.5682 50 1.6990-0.1308 0.01710 186 2.2695 167 2.2227 0.0468 0.00219 218 2.3385 258 2.4116-0.0732 0.00535 200 2.3010 243 2.3856-0.0846 0.00715 39 1.5911 54 1.7324-0.1413 0.01997 217 2.3365 180 2.2553 0.0812 0.00659 119 2.0755 133 2.1239-0.0483 0.00233 28 1.4472 46 1.6628-0.2156 0.04648 106 2.0253 112 2.0492-0.0239 0.00057 107 2.0294 89 1.9494 0.0800 0.00640 45 1.6532 62 1.7924-0.1392 0.01937 98 1.9912 128 2.1072-0.1160 0.01345 240 2.3802 220 2.3424 0.0378 0.00143 32 Reproducibility Replicates Step 1 Transform the raw data by taking the log base 10 value (log 10 ) of the data (column 2, 4). Step 2 Calculate the overall mean of 40 results in columns 2 and 4, this is 1.9219. Step 3 Calculate the difference between the transformed replicates (column 5) then square the differences between the transformed replicates (column 6). Step 4 Add the differences together (column 6) and divide by 2n, where n = the total number of pairs of duplicates (for this example n = 20) to get 0.00919. 33 11

Reproducibility Replicates Step 5 Take the square root of the result in step 4; this equals the pooled reproducibility standard deviation, which is 0.0959. Step 6 Convert this standard deviation into a relative standard deviation (RSD) by dividing by the mean (1.9219) from Step 2, which produces an RSD of.0499. (e.g., 0.0959 1.9219= 0.0499) Step 7 Apply the coverage factor (k=2 for 95% coverage) to the RSD to get the estimate of the expanded uncertainty, 0.0998 (Note this is a log 10 value). (e.g., Ue= 2 x 0.0499= 0.0988) If using the student t-tables, with n=20 (19 degrees of freedom), k would be 2.09, which would provide an relative expanded uncertainty of 0.1043. 34 Reproducibility Replicates Step 9 To calculate the uncertainty for any subsequent laboratory result, the subsequent result is first converted to the log base 10 value (log 10 ), multiplied by 0.0998 and then this expanded uncertainty is added and subtracted from the log 10 value. Step 10 To estimate the MU of a sample, convert the log value for the sample measurement back to CFU for the reported result. This is accomplished by taking the anti-log of each of the endpoints of the interval (anti-log of x = 10 x ). For example, using a result of 150 CFU: 150 in log 10 = 2.1761. The relative Ue (rue) in log counts is 0.2172 (2.1761 x 0.0998). Add and subtract rue from 2.1761 gives an interval from 1.9589 to 2.3933; transformed back to counts: 10 1.9589 =90.97, and 10 2.3933 = 247.33. Therefore the uncertainty interval is 90 to 248 CFU. 35 Recovery replicates The same amount of inoculum plated both with/without matrix. The sources of uncertainty are reflected in the difference between different sets of replicates. A single SD is calculated as the estimate of combined standard uncertainty. 36 12

Recovery replicates CFU Inoculated Log 10 Value CFU recovered in Spike Log 10 Value % Recovery of Log Values X=97.0% SD=3.6% Column 1 Column 2 Column 3 Column 4 Column 5 30,000 4.4771 20,000 4.3010 96.1 17,000 4.2304 12,000 4.0792 96.4 36,000 4.5563 49,000 4.6902 102.9 150 2.1761 90 1.9542 89.8 2,400 3.3802 1,300 3.1139 92.1 43,000 4.6335 32,000 4.5051 97.2 100 2.0000 98 1.9912 99.6 42,000 4.6232 31,000 4.4914 97.1 19,000 4.2788 12,000 4.0792 95.3 100 2.0000 120 2.0792 104.0 580,000 5.7634 410,000 5.6128 97.4 2,500 3.3979 2,000 3.3010 97.1 1,100 3.0414 930 2.9685 97.6 18,000 4.2553 12,000 4.0792 95.9 2,000 3.3010 1,900 3.2788 99.3 1,700 3.2304 2,100 3.3222 102.8 2,100 3.3222 1,700 3.2304 97.2 150 2.1761 100 2.0000 91.9 2,000 3.3010 1,600 3.2041 97.1 150 2.1761 110 2.0414 93.8 Mean % Recovery = 97.0% SD = 3.6% 37 Recovery replicates Step 1 Transform the CFU values (columns 1, 3) to log base 10 value (log 10 ) (columns 2, 4). Step 2 Calculate the % recovery of the log 10 values by dividing column 4 by column 2 and multiplying by 100 (column 5). Step 3 Calculate the mean and standard deviation (SD) of the % recovery of the log 10 values. The mean recovery is 97.0% and the SD of % recovery is 3.6%. The SD is an estimate of the combined standard uncertainty, which can be used as a relative uncertainty. 38 Recovery replicates Step 4 For reporting purposes, apply the coverage factor to the SD to obtain Ue. For 95% coverage we use a coverage factor of k=2. The expanded uncertainty in this example is thus 7.2%. (If using the student t-tables, with n=20 (19 degrees of freedom), the coverage factor k would be 2.09, which would provide an expanded uncertainty of 7.5%.) Step 5 Because the recovery is expressed as a percentage, when calculating the expanded uncertainty for a sample, this percentage needs to be multiplied by the log 10 value in order to estimate the uncertainty in log units. For example, for a result of 150 CFU: 150 in log 10 = 2.1761. The Ue in log counts is 0.1567 (2.1761 x 0.072). Add and subtract Ue from 2.1761 gives an interval from 2.0194 to 2.3328; transforming back to counts: 10 2.0194 =104.6, and 10 2.3328 = 215.2. Therefore the uncertainty interval is 104 to 216 CFU. 39 13

Most Probable Number data 40 Measurement uncertainty MPN LCS results should be used provided these are an appropriate matrix and concentration. If all method steps are included, can use SD or RSD. If <20 LCS results, the CF should be the appropriate t statistic for 95% confidence for the associated DF. The estimate of combined uncertainty is then expanded using the formula: MPN MU(LCS) = k x SD, where k equals 2 (for 95% confidence). 41 Most Probable Number, FDA Bacteriological Analytical Manual For 3 tubes each at 0.1, 0.01, and 0.001 g inocula, the MPNs per gram and 95 percent confidence intervals. Pos. tubes Conf. lim. Pos. tubes Conf. lim. MPN/g MPN/g 0.10 0.01 0.001 Low High 0.10 0.01 0.001 Low High 0 0 0 <3.0 9.5 2 2 0 21 4.5 42 0 0 1 3.0 0.15 9.6 2 2 1 28 8.7 94 0 1 0 3.0 0.15 11 2 2 2 35 8.7 94 0 1 1 6.1 1.2 18 2 3 0 29 8.7 94 0 2 0 6.2 1.2 18 2 3 1 36 8.7 94 0 3 0 9.4 3.6 38 3 0 0 23 4.6 94 1 0 0 3.6 0.17 18 3 0 1 38 8.7 110 1 0 1 7.2 1.3 18 3 0 2 64 17 180 1 0 2 11 3.6 38 3 1 0 43 9 180 1 1 0 7.4 1.3 20 3 1 1 75 17 200 1 1 1 11 3.6 38 3 1 2 120 37 420 1 2 0 11 3.6 42 3 1 3 160 40 420 1 2 1 15 4.5 42 3 2 0 93 18 420 1 3 0 16 4.5 42 3 2 1 150 37 420 2 0 0 9.2 1.4 38 3 2 2 210 40 430 2 0 1 14 3.6 42 3 2 3 290 90 1,000 2 0 2 20 4.5 42 3 3 0 240 42 1,000 2 1 0 15 3.7 42 3 3 1 460 90 2,000 2 1 1 20 4.5 42 3 3 2 1100 180 4,100 2 1 2 27 8.7 94 3 3 3 >1100 420 42 14

Laboratory Control Data with Same Target Value (e.g., 100 CFU) MPN value Predicted CFU Log 10 Value (Pos. Tubes) SD= 0.2943 2 2 2 35 1.5441 2 3 1 36 1.5563 3 1 3 160 2.2041 3 1 2 120 2.0792 3 2 0 93 1.9685 3 2 1 150 2.1761 3 2 2 210 2.3222 3 1 1 75 1.8751 3 1 0 43 1.6335 3 3 0 240 2.3802 3 0 2 64 1.8062 3 1 1 75 1.8751 3 1 2 120 2.0792 3 0 2 64 1.8062 2 1 2 27 1.4314 3 1 2 120 2.0792 3 2 3 290 2.4624 3 1 3 160 2.2041 3 0 2 64 1.8064 43 Measurement uncertainty MPN Step 1 Locate the MPN predicted CFU based on the number of positive tubes Step 2 Transform the CFU values to log 10 value. Step 2 Calculate the SD of the log 10 values. SD= 0.2943. Step 3 Apply the coverage factor (95%, k=2) to the SD to obtain Ue. The Ue in this example is 0.5886. (Students t table with n=20 = 2.09. Ue =0.6151 44 Measurement uncertainty MPN Step 4 To calculate the uncertainty for any subsequent laboratory result using SD x k, the result is first converted to log base 10 value (log 10 ), and the expanded uncertainty of 0.5586 is added and subtracted from the log value. Step 5 - Convert the log value for the sample measurement back to CFU for the reported result. This is accomplished by taking the anti-log of each of the endpoints of the interval (anti-log of x = 10 x ). For example, estimating the uncertainty using SD x k for a result of 160 CFU: 160 in log 10 = 2.2041. Adding and subtracting 0.5886 from 2.2041 gives an interval from 1.6155 to 2.7927; transforming back to counts: 10 1.6155 =41.27, and 10 2.7927 =620.44. Therefore the uncertainty interval is 41 to 621 CFU. 45 15

Acknowledgements A2LA G108 Guidelines for Estimating Uncertainty for Microbiological Counting Methods By Dawn Mettler and Dan Tholen And personal communication 46 Questions / Comments 47 For Further Information Contact: Roger M. Brauninger Phone: 301 644 3233 Email: rbrauninger@a2la.org American Association for Laboratory Accreditation 5301 Buckeystown Pike, Suite 350 Frederick, MD 21704 www.a2la.org 48 Comments/concerns about this program? Email: webinar@aphl.org 16