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National Office of Pollution Prevention
Table of Contents
Abstract
Summary
1. Introduction
2. Monitoring/Direct Measurement of Releases
3. Analytical Methods
4. Quality Assurance/Quality Control
5. Estimation of Releases
6. Reporting
7. Validation / Verification
Glossary of Terms and Acronyms
References
Bibliography
Appendix A: Standardized Release Reporting Template
Appendix B: Error Estimation
Appendix C: US EPA AP-42 Emission Factors
GUIDANCE DOCUMENT FOR REPORTING OF RELEASES FROM THE BASE METALS SMELTING SECTOR

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APPENDIX B ERROR ESTIMATION

Table of Contents

  1. 1. GENERAL
  2. 2. ERROR PROPAGATION FORMULAE
    1. 2.1 Addition/Subtraction of Two Variables
    2. 2.2 Multiplication/Division of Two Variables
  3. 3. EXAMPLE OF ERROR CALCULATION FOR DIRECT MEASUREMENT
  4. 4. EXAMPLE OF ERROR CALCULATION FOR MASS BALANCE

1. General

The error of an individual measurement can be estimated by the using the standard deviation for the measurement device, for example, a scale may be accurate to ± 100 kg or a laboratory device may measure concentration ± 2%.

Two measured variables (e.g., flow F and concentration C) with uncertainties (∆F and ∆C) might then be used to calculate a new value, Releases (R). The error of the release estimate (∆R) can be calculated using traditional statistical techniques.

This appendix provides basic formulae with examples as well as examples of error estimation for direct measurement and mass balance release calculations.

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2. Error Propagation Formulae

Two measured variables (e.g., x and y) with uncertainties (∆x and ∆y) might be used to calculate a new value, z. The following two subsections provide formulae which are used to calculate the uncertainty, ∆z in z for addition/subtraction and multiplication/division.

2.1 Addition/Subtraction of Two Variables

The following formula is typically used to determine the variance of the sum of two values, the variances of which are known:

∆z = SQRT [(∆x)2 + (∆y)2]

where:

  • ∆z is the error for the sum
  • ∆x is the error for the first variable
  • ∆y is the error for the second variable

For example, if

    x = 2.0 ± 0.2 cm

    y = 3.0 ± 0.6 cm

and,

    z = x + y = 2.0 cm + 3.0 cm = 5.0 cm

then,

    ∆z = SQRT [(0.2 cm)2 + (0.6 cm)2] = 0.6 cm

therefore,

    z = 5.0 ± 0.6 cm

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2.2 Multiplication/Division of Two Variables

The following formula is typically used to determine the variance of the product of two values, the variances of which are known:

∆z/z = SQRT [(∆x/x)2 + (∆y/y)2]

For example, if

    x = 2.0 ± 0.2 cm

    y = 3.0 ± 0.6 cm

and,

    z = x * y = 2.0 cm * 3.0 cm = 6.0 cm2

then,

    ∆z/z = SQRT [0.2/2.0)2 + (0.6/3.0)2] = 0.22

    ∆z = 0.22 * 6.0 cm2= 1.3 cm2

therefore,

    z = 6.0 ± 1.3 cm2

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3. Example of Error Calculation for Direct Measurement

If a facility was calculating particulate matter emissions based on a measurement of flow in a particular stack and the particulate matter concentration, the following information might be available:

Flow: 2,000 m3/min with an estimated error of 100 m3/min

Concentration: 15 mg/m3 with an estimated error of 1.5 mg/m3

Operating hours: 16 hours a day, 340 days in the year.

The releases of particulate matter (PM) is calculated as follows:

PM = 15 mg/m3 * 2,000m3/min * 60 min/hour * 1X10-6kg/mg * 16 hours/day * 340 days/year * 0.001 tonnes/kg = 9.8 tonnes/year

The error is calculated using the error estimated for each variable and the formula provided in the preceding section.

    ∆PM/PM = SQRT [(100/2,000)2 + (1.5/15)2]

    = 0.11

This error can then be converted into an absolute value by multiplying the error by the release estimate.

    ∆PM = 9.8 tonnes/year * 0.11 = 1.1 tonnes per year

The particulate matter, for this facility is therefore, 9.8 ± 1.1 tonnes.

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4. Example of Error Calculation for Mass Balance

If a facility is calculating its sulphur dioxide release using mass balance, the following information might be available:

Table 4-1: Mass and Concentration of Sulphur in Each Stream - Mass Balance Example with Error Estimates

Stream

Mass of Stream
(tonnes)

Error Estimate
(%)

Concentration of Sulphur
(%)

Error Estimate
(%)

Concentrate

30,000

1%

30

0.3%

Recyclables

3,000

2%

5

5%

Other

1,500

5%

5

5%

Product

7,500

0.5%

15

1%

Slag

25,000

10%

1

10%

By-product (sulphuric acid)

20,000

0.5%

32

0.5%

The mass of sulphur in each stream and the calculated error is provided in the table below:

Table 4-2: Mass of Sulphur in Each Stream - Mass Balance Example

Stream

Mass of Sulphur in Stream
(tonnes)

∆S/S
(square root of sum of errors squared)

Standard Error
(tonnes)

Concentrate

9,000

0.0104

94.0

Recyclables

150

0.0539

8.1

Other

75

0.0707

5.3

Total Input

9,225

 

 

Product

1,125

0.0112

12.6

Slag

250

0.1414

35.4

By-product (sulphuric acid)

6,400

0.0071

45.3

Total Output

7,775

 

 

The error on each of the input and output streams is equal to the square root of the sum of the errors squared as shown in the tables below.

Table 4-3: Error Estimation on Input Streams

Stream

Standard Error
(tonnes)

Standard Error Squared

Concentrate

94.0

8,829

Recyclables

8.1

65

Other

5.3

28

Sum of Standard Errors Squared

 

8,922

Standard Error of Sum
(tonnes) sulphur

 

94



Table 4-4: Error Estimation on the Output Streams

Stream

Standard Error
(tonnes)

Standard Error Squared

Product

12.6

158

Slag

35.4

1,250

Sulphuric Acid

45.3

2,048

Sum of Standard Errors Squared

 

3,456

Standard Error of Sum
(tonnes) sulphur

 

59

The error for the emission calculation is calculated as shown in Table 4-5.

Table 4-5: Error Estimation on the Annual Release

 

Sulphur
(tonnes)

Standard Error
(tonnes)

Standard Error Squared

Total Inputs

9,225

94

8,922

Total Outputs

7,775

59

3,456

Releases

1,450

 

 

Sum of standard errors squared

 

 

12,379

Standard Error of Sums
(tonnes sulphur)

 

 

111

Standard Error (%)

 

 

7.7

If this mass balance calculation estimates the monthly emissions, an additional calculation is required to determine standard error on an annual basis. The error is divided by the square root of 12 (i.e., the number of data points) to yield an error on an annual basis of 2.2%

The calculated standard error can then be multiplied by 2 to yield a 95.5% confidence limit. The annual error at 95.5% confidence would be ± 4.4%.

In order to yield an absolute error value, this percentage is multiplied by the annual release.

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