MEMORANDUM
TO: Docket EPA-HQ-OAR-2002-0058
FROM: Peter Westlin, EPA/OAQPS/SPPD
DATE: January 20, 2011
SUBJECT: Measurement Imprecision for Carbon Monoxide

A. INTRODUCTION EPA received many comments about the overall stringency of the carbon monoxide (CO) emission limits in the proposed boiler MACT rule. Some of the comments focused on measurement error associated with the analyzers that are used to quantify CO concentrations. This memorandum presents the findings of EPA’s analysis.

B. DISCUSSION For low CO levels measured using EPA Met hod 10, we reviewed the quality of the data relative to information provided fo r each emissions test. Method 10 is structured such that we can assess measurement data quality relative to the calibration span of the instrument. 1,2 For example, the allowable calibration error, syst em bias, and drift requirements are directly proportional to the site-specific instrument calib ration span (i.e., ± 2.0 pe rcent of the calibration span value). For instrument calibration sp an values of 25 ppmv and less, the allowable calibration error, bias, or drif t values are each ± 0.5 ppmv.

We can estimate the equivalent of the met hod detection level for a measurement with an instrumental test method (e.g., EPA Methods 3A, 6C, 7E, 10, and 25A) including the measurement of CO emissions using a square root formula and these method prescribed allowable data quality criteria. For example, in the case of a calibration span value of 25 ppmv, the square root formula (i.e., square r oot of the sum of the squares, or (0.5 2 +0.5 2 +0.5 2 )^ 1/2 ) would indicate a value of 0.9 ppmv as th e instrument detecti on level. Consiste nt with the methodology we applied for non-instrumental methods, discusse d in section C of this memorandum, where we established limits no less than three times the MDL, this estimated measurement error value ofabout 1 ppmv would translate a lim it of 3 ppmv. For tests done w ith calibration sp ans of greater than 25 ppmv, the corresponding estimated measurem ent error would be greater. For example,
the estimated measuremen t error using the square root fo rmula for a calibration span of 100 ppmv would be about 4 ppmv wh ich would translate to a limit of 12 ppmv. For a calibration span of 1000 ppmv, the estimated measurement e rror would be 35 ppmv or a limit of about 100

ppmv.

One outcome of this assessment is rec ognition that the site-specific estimated
measurement errors in some cases may be higher than some of th e reported levels. Therefore,
for each emission test used in the MACT floor calculations we substituted the site-specific estimated measurement error for reported values below those values in order to ensure the quality of the data us ed to set the floors.

C. MEASUREMENT IMPRECISION AT OR NEAR THE METHOD DETECTION
LEVEL For the boiler and process heater source cat egory, which includes many sources with
emission levels at or near the method detecti on levels (MDLs) for the various pollutants, measurement imprecision is a significant factor that should be included in the development of emission limits for boilers and process heaters. To determine an appropriate methodology, EPA
examined the contribution of test method measurem ent imprecision to the va riability of a set of emissions data. One element of variability is associated with method de tection capabilities and a
second is a function of the measurement valu e. Measurement imprecision is proportionally highest for values measured below or near a method’s detection level and proportionally decreasing for values measured a bove the method detection level. The probability procedures applied in calculating the floor or an emissions limit inherently and reasonably account for emissions data variability in cluding measurement imprecision when the database represents multiple tests from multiple emissions units for which all of the data are measured significantly above the method detection level. That is less true
when the database includes emissions occurri ng below method detection capabilities and are reported as the method detection level values. EPA’s guidance to respondents for reporting po llutant emissions used to support the datacollection specified the criteria for determining test-speci fic method detection levels. Those criteria insure that there is only about a 1 per cent probability of an erro r in deciding that the pollutant measured at the method detection level is present when in fact it was absent. Such a probability is also called a false positive or the alpha, Type I, error. Because of sample and emissions matrix effects, laborat ory techniques, sample size, and other factors, method detection levels normally vary from test to test for any specific test method and pollutant measurement. The expected measurement imprecision for an emi ssions value occurring at or near the method detection level is about 40 to 50 percent. Po llutant measurement imprecision decreases to a consistent relative 10 to 15 per cent for values measured at a level about three times the method
detection level. 3 Also in accordance with our guidance, source owners identified emissions data which
were measured below the method detection leve l and reported those valu es as equal to the
method detection level as determined for that test. An effect of reporting data in this manner is that the resulting database is truncated at the lo wer end of the measurement range (i.e., no values reported below the test-specific method detection level). A floor or emissions limit based on a
truncated database or otherwise including values measured near the method detection level may not adequately account for measurement imprecision co ntribution to the data variability. That is,
an emission limit set based on the use of the MD L to represent data below the MDL may be significantly different than the actual levels achieved by the best performing units due to the imprecision of the measurements. This fact, combined with the low levels of emissions measured from many of the best performing units, led EPA to develop a procedure to account for
the contribution of measurement imprecision to data variability. We applied the following procedures to account for the effect of measurement imprecision associated with a database that includ es method detection level data. The first step
is to define a method detection le vel that is representative of th e data used in establishing the
floor or emissions limit and that also minimizes the influence of an outlier test-specific method detection level value. We reviewed each pollutant -specific data set to identify the highest testspecific method detection level repor ted that was also equal to or less than the average emissions level (i.e., unadjusted for probabili ty confidence level) calculated for the data set. We believe that this approach is representative of the data collected to develop the floor or emissions limit while to some degree minimizing the effect of a test(s) with an inordinately high methoddetection level (e.g., the sample volume was too small, the laboratory technique was insufficiently sensitive, or the procedure for dete rmining the detection level was other than that specified). The second step in the process is to calcu late three times the representative method detection level and compare that value to the calculated floor or emissions limit. If three times the representative method detection level were le ss than the calculated floor or emissions limit calculated from the upper prediction limit (UPL), we would conclude that measurement variability was adequately addressed because th e measurement inprecision at that level is a consistent 10 to 15 percent. The calculated fl oor or emissions limit would need no adjustment. If, on the other hand, the value eq ual to three times the representative me thod detection level were greater than the UPL-based emission limit, we would conclude that the calculated floor or emission limit does not account entirely for measurem ent variability. If i ndicated, we substituted the value equal to three times the representative method detection level to apply as the adjusted floor or emissions limit. This adjusted value w ould ensure measurement va riability is adequately
addressed in the floor or the emissions limit.

REFERENCES

1. Environmental Protection Agency. Emissi on Measurement Center. "Test Method 7E: Determination of Nitrogen Oxides Emissions from Stationary Sources (Instrumental Analyzer Procedure)." November 2008. <http://www.epa.gov/ttn/emc/promgate/method7E.pdf>.

2. Environmental Protection Agency. Emissi on Measurement Center. "Test Method 10:
Determination of Carbon Monoxide Emissions from Stationary Sources (Instrumental Analyzer Procedure)." <http://www. epa.gov/ttn/emc/promgate/method10r06.pdf>

3. American Society of Mechanical Engineers, Reference Method Accuracy and Precision (ReMAP): Phase 1, Precision of Manual Stack Emission Measurements , CRTD Vol. 60, February 2001.