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Control of Volatile Organic Compounds Emissions from Manufacturing

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The principle underlying the Byron method is the same as EPA<br />

Method 25. However, rather than using a modified standard GC, the<br />

Byron method uses a process analyzer. This instrument speciates C2<br />

<strong>from</strong> higher hydrocarbons, but gives a single value for all nonmethane<br />

hydrocarbons. After separation, a1 1 carbonaceous material is combusted<br />

to C02 which is then converted to CH4 before being measured by an FID.<br />

Thus, the variable response <strong>of</strong> the FID to different types <strong>of</strong> organics<br />

is eliminated in the Byron 401 as it is in EPA Method 25.<br />

The oxides <strong>of</strong> nitrogen (NOx) content <strong>of</strong> the flue gas was determined<br />

using the methodology specified in EPA Method 7. A detailed description<br />

<strong>of</strong> a11 these sampling and analytical techniques can be found in the<br />

ARC0 test report.<br />

The total flue gas flow rate was determined two or three times<br />

daily using procedures described in EPA Method 2. Based on this<br />

method, the volumetric gas flow rate was determined by measuring the<br />

cross-sectional area <strong>of</strong> the stack and the average velocity <strong>of</strong> the flue<br />

gas. The area <strong>of</strong> the stack was determined by direct measurements.<br />

The work performed during this program incorporated a comprehensive<br />

quality assurance/quality control (QA/QC) program as an integral part<br />

<strong>of</strong> the overall sampling and analytical effort. The major objective <strong>of</strong><br />

the QA/QC program was to provide data <strong>of</strong> known qua1 ity with respect to<br />

completeness, accuracy, precision, representativeness, and comparability.<br />

D.2.1.3 Test Results. The VOC measurements were made by at<br />

least four <strong>of</strong> five independent methods for each <strong>of</strong> eight different<br />

combinations <strong>of</strong> incinerator temperature and waste streams. Tab1 e D-5<br />

summarizes the results <strong>of</strong> measured destruction efficiencies (DE's) for<br />

each <strong>of</strong> these condi tions.<br />

The results indicate that the values for the DE's by Method 25<br />

are consistently lower and <strong>of</strong> poorer quality. The poorer quality is<br />

indicated by the imprecision reflected by the much larger standard<br />

deviations for this measurement method. The accuracy and representa-<br />

tiveness <strong>of</strong> these values obtained <strong>from</strong> Method 25 is, thus, questionable.<br />

If Method 25 results are disregarded, the DE's for all testing combinatio<br />

are found to be consistently above 99 percent.

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