assessing laboratory quality – systematic bias

21
Assessing Laboratory Quality – Systematic Bias Robert O. Miller Colorado State University Fort Collins, CO

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Assessing Laboratory Quality – Systematic Bias. Robert O. Miller Colorado State University Fort Collins, CO. Method Performance. Soil Analysis Bias and Precision. Bias (accuracy) and precision is best depicted by the target bulls eye. - PowerPoint PPT Presentation

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Page 1: Assessing Laboratory Quality – Systematic Bias

Assessing Laboratory Quality – Systematic Bias

Robert O. MillerColorado State University Fort Collins, CO

Page 2: Assessing Laboratory Quality – Systematic Bias

Miller, 2013

Method Performance

Bias (accuracy) and precision is best depicted by the target bulls eye.

Soil Analysis Bias and Precision

Bias evaluates soil test consistency between labs, important to the industry, whereas precision defines the uncertainty of the soil test within a laboratory.

http://www.amrl.net/AmrlSitefinity/Newsletter/images/Spring2012/5_image%201.jpg

Page 3: Assessing Laboratory Quality – Systematic Bias

Assessing BiasSoil Analysis Bias and Precision

Assessment of lab method bias is can be achieved through certified reference samples and/or lab proficiency samples.

Bias can be random, indicating no pattern across multiple reference samples, or systematic in one direction. Bias can be concentration dependent.

Laboratory corrective actions is dependent on the type of bias encountered.

Miller, 2013

Page 4: Assessing Laboratory Quality – Systematic Bias

Proficiency Reports

Miller, 2013

With the completion of each ALP cycle a report is prepared for each lab participant. Soil test results with values exceeding a 95% confidence limit are flagged and precision flagged for samples exceeding 3 x Rd.

Page 5: Assessing Laboratory Quality – Systematic Bias

Consensus Value: pH (1:1) H2O

Miller, 2013

Lab Rank

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40

pH

(1:1

) H

2O

4.0

4.5

5.0

5.5

6.0

6.5

7.0

7.5

8.0

8.5

SRS-1111SRS-1112SRS-1113SRS-1114 SRS-1115

Lab #1 Systematic Bias

1 Results ranked from low to high based on soil SRS-1111.

Page 6: Assessing Laboratory Quality – Systematic Bias

Miller, 2013

Soil Proficiency Observations - pH

2012 data was compiled for sixteen Illinois labs across 15 soils. Individual lab reports were provided to participants.

Deviation and regression plots provide information systematic bias across 15 soils ranging from pH 5.29 to 7.86.

Deviation plots indicate absolute differences for individual samples, whereas regression plots show an overall comparison for the year.

SRS-1201

SRS-1202

SRS-1203

SRS-1204

SRS-1205

SRS-1206

SRS-1207

SRS-1208

SRS-1209

SRS-1210

SRS-1211

SRS-1212

SRS-1213

SRS-1214

SRS-1215

-0.25-0.20-0.15-0.10-0.050.000.050.100.150.200.25

Deviation Plot

pH

Dev

iati

on

Soil ID

Page 7: Assessing Laboratory Quality – Systematic Bias

Lab ID pH (1:1)Slope Intercept R2

U6304A 0.97 0.05 0.998

U6322A 0.98 0.12 0.980

U6333A 0.95 0.31 0.997

U6336A 0.97 0.24 0.994

U6353A 1.11 -0.73 0.991

U6718A 0.95 0.34 0.994

U6835A 0.94 0.47 0.985

U6874A 1.01 -0.08 0.999

Source: ALP 2011 database. Eight of 48 labs shown.

Miller, 2013

Laboratory PerformanceRegression Analysis pH, 2011 1

Regression analysis provides insight on lab method bias.

An evaluation of soils with pH 4.98 - 8.10 slope shows 1 of 8 labs deviate by > 5% from the median for the 2011 ALP soils.

Regression intercepts deviated > 0.35 units for 2 of 8 labs shown.

Page 8: Assessing Laboratory Quality – Systematic Bias

Laboratory Performance

A year summary provides insight on lab method bias.

Results for lab U7255A show random deviations at top left.

Lab U6388A, lower left, consistent low bias across all PT cycles.

Deviation Plot Mehlich 1-P, 1

1 Source: ALP 2012 database. Soil M1-P values range 2 - 255 ppm.

SRS-1201SRS-1202SRS-1203SRS-1204SRS-1205SRS-1206SRS-1207SRS-1208SRS-1209SRS-1210SRS-1211SRS-1212SRS-1213SRS-1214SRS-1215

-30

-20

-10

0

10

20

30Lab U6288A

M1

-P

Dev

iati

on

pp

m

Soil ID

SRS-1201SRS-1202SRS-1203SRS-1204SRS-1205SRS-1206SRS-1207SRS-1208SRS-1209SRS-1210SRS-1211SRS-1212SRS-1213SRS-1214SRS-1215

-30

-20

-10

0

10

20

30 Lab U7225A

M1

-P

Dev

iati

on

pp

m

Soil ID

255 ppm

Page 9: Assessing Laboratory Quality – Systematic Bias

Laboratory PerformanceDeviation Mehlich 3-P ICP

Miller, 2013

Lab U6289A indicates deviations in 2012 cycle 17, none in cycle 18 and bias high deviations in cycle 19.

Lab U7135A indicates significant high bias deviations on two of fifteen samples – these had M3-P concentrations > 150 ppm.

SRS-1201

SRS-1202

SRS-1203

SRS-1204

SRS-1205

SRS-1206

SRS-1207

SRS-1208

SRS-1209

SRS-1210

SRS-1211

SRS-1212

SRS-1213

SRS-1214

SRS-1215

-30.0

-20.0

-10.0

0.0

10.0

20.0

30.0

Lab ID U6289A

M3-

P

ICP

D

evia

tio

n p

pm

SRS-1201

SRS-1202

SRS-1203

SRS-1204

SRS-1205

SRS-1206

SRS-1207

SRS-1208

SRS-1209

SRS-1210

SRS-1211

SRS-1212

SRS-1213

SRS-1214

SRS-1215

-30.0

-20.0

-10.0

0.0

10.0

20.0

30.0

Lab ID U7135M

3-P

IC

P

Dev

iati

on

pp

m

1 Source: ALP 2012 database. Soil M3-P ICP values range 1 - 166 ppm.

Page 10: Assessing Laboratory Quality – Systematic Bias

Laboratory Performance

Deviation Plot M3-K

Miller, 2013

SRS-1201

SRS-1202

SRS-1203

SRS-1204

SRS-1205

SRS-1206

SRS-1207

SRS-1208

SRS-1209

SRS-1210

SRS-1211

SRS-1212

SRS-1213

SRS-1214

SRS-1215

-30.0

-20.0

-10.0

0.0

10.0

20.0

30.0

Lab ID U6289A

M3-

K

Dev

iati

on

pp

m

SRS-1201

SRS-1202

SRS-1203

SRS-1204

SRS-1205

SRS-1206

SRS-1207

SRS-1208

SRS-1209

SRS-1210

SRS-1211

SRS-1212

SRS-1213

SRS-1214

SRS-1215

-30.0

-20.0

-10.0

0.0

10.0

20.0

30.0

Lab ID U7135AM

3-K

D

evia

tio

n p

pm

Lab U6289A indicates high bias deviations in 2012 cycle 17, none in cycle 18 and general two of five in cycle 19.

Lab U7135A indicates general low bias deviations across all samples independent of concentration.

1 Source: ALP 2012 database. Soil M3-K values range 39 - 502 ppm.

Page 11: Assessing Laboratory Quality – Systematic Bias

Multiple Flags ( 2-5 )Single Flag

* Bias Flag(s)

- Random Error- Near Detection Limit - Dilution Error - Transcription Error- Problematic Sample

Both Low and High Bias

High Bias at Low Concentration

High Bias at allConcentrations

Low Bias at allConcentrations

Low Bias at low Concentrations

Evaluating Laboratory Bias

Miller, 2013

High Bias at High Concentration

Low Bias at high Concentrations

Evaluation based on assessment of five proficiency soils.

Dominant High Bias

Equal High and Low Bias

Consistent Low Bias

Consistent High Bias

Page 12: Assessing Laboratory Quality – Systematic Bias

Multiple Flags ( 2-5 )

Low Bias at allConcentrations

Low Bias at low Concentrations

Low Bias at high Concentrations

Consistent Low Bias

Both Low and High Bias

Consistent High Bias

- Verify calibration Stds- Verify extractant volume- Check extractant Conc.

- Verify calibration Stds- Verify extractant volume- Check Extractant Conc.

Evaluating Laboratory Bias

Miller, 2013

- Verify low calibration Stds- Verify extractant volume- Check extractant Conc.

Systematically evaluate each component of the analysis, extraction, analysis and reporting relative to low bias.

Page 13: Assessing Laboratory Quality – Systematic Bias

Multiple Flags ( 2-5 )

Consistent Low Bias

Both Low and High Bias

Consistent High Bias

- Check for Contamination - Verify calibration stds- Check extractant Conc.- Verify MDL

- Verify calibration Stds- Verify extractant volume- Check Extractant Conc.

Evaluating Laboratory Bias – Cont.

Miller, 2013

- Check for Contamination - Verify low calibration Stds- Verify extractant volume- Check extractant Conc.

High Bias at Low Concentration

High Bias at allConcentrations

High Bias at High Concentration

Systematically evaluate each component of the analysis, extraction, analysis and reporting relative to high bias.

Page 14: Assessing Laboratory Quality – Systematic Bias

Determining Method Bias Components

Cause-and-effect diagrams are used to systematically list

the different component sources which contribute to total of

bias in the analysis results. A cause-and-effect diagram

can aid in identifying those sources with the greatest

contribution.

Miller, 2013

Test Result

“Ishikawa

Diagram”

Page 15: Assessing Laboratory Quality – Systematic Bias

Miller, 2013

Extraction

Instrument

Test Result

ExtractantShaker

Operation

Fish-Bone Diagram of Soil M3-P Analysis

Extract Volume

Use Component Factor Analysis to Assess Bias

* Major Components

Calibration

SampleHomogeneity

Degree of Mixing

Filter

Stability

Scoop

Technique

Time

Carry Over

Page 16: Assessing Laboratory Quality – Systematic Bias

Miller, 2013

Extraction

Instrument

Test Result

Stirring

Electrode

Fish-Bone Diagram of Soil pH (1:1) H2O

Volume

Calibration

SampleHomogeneity

Degree of Mixing

Stability

Scoop

Technique Carry Over

Bias Components

- pH Calibration

- Electrode

- Other?

Page 17: Assessing Laboratory Quality – Systematic Bias

0 1000 2000 3000 4000 5000 60000

1000

2000

3000

4000

5000

6000

ALP Ca (ppm) Median

La

b M

3-C

a (

pp

m)

Me

an

Number 15Minimum 480Maximum 5700Slope 1.20Intercept -344R2 0.980

Example Bias AssessmentPlot M3-Ca

Miller, 2013

Lab U6816A

Fifteen soils ranging from 609-5100 ppm Ca, show significant systematic bias, trending low on soils with low M3-Ca and high on high testing soils. Best shown with regression with slope of 1.20, intercept is -344.

Low bias on low soils, high bias on high soils.

Source of Bias?

(1:1 line)

Page 18: Assessing Laboratory Quality – Systematic Bias

Diagram of Mehlich 3 Ca – Lab U6816A

Bias ComponentsExtraction

Analysis

Bias of Result

Reagent

Filter Time

Temperature

Volume

Calibration

Stability

Filter Paper

Homogeneity

ScoopDegree of Mixing

TechniqueICP

Carry Over

For Ca, values in red may contribute to bias.

Contamination

Miller, 2013

Shaker

- Calibration Standards

- Reagent pH, Concentration

- Instrument Carryover

- Other?

WavelengthNumber

Page 19: Assessing Laboratory Quality – Systematic Bias

Miller, 2013

Review bias results and develop a check off list as to extraction and analysis components which contribute to bias as it relates to concentration.

From this list develop a systematic to assess source of bias analytical results.

Example Bias AssessmentCheck off List

ParameterMethod

Component Extraction

Extractant Conc.

Extractant Volume

Contamination

Shaker

Filter Paper

Filtration Time

Analysis

Page 20: Assessing Laboratory Quality – Systematic Bias

Quality Flossing

Miller, 2013

Like dental hygiene, one should periodically assess your lab’s QC program effectiveness.

Through a review of PT program results, use of external standards, and double blind evaluations it’s good lab practice to evaluate lab bias and precision and make modifications to the QC program.

Page 21: Assessing Laboratory Quality – Systematic Bias

Thank you for your time and Attention