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Alloy x331 Driver

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Alloy x331 Driver

This indicates an emission rate of approximately Ib. All procedures were essentially the same as those being issued by the Environmental Protection Agency for source sampling. Preliminary velocity and temperature readings were obtained in order to select Alloy x331 sizes for isokinetic sampling.

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Particulate sampling was. Gas sampling was also conducted in accordance with the proposed EPA standard source ttsting methods.

Sulfur dioxide was sampled with midget impingers using isopropyl alcohol and Alloy x331 peroxide solutions. Combustion gases were sampled in plastic bags for immediate analysis with an Orsat analyzer. Particle sizing was carried out using Brink cascade impactor collec- tors.

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Alloy x331 Sampling for metals analysis was conducted using the OAP train with glass probe, without Alloy x331 cyclone collector. Only the material collected on the filter was saved for analysis. Basically the Alloy x331 is accomplished using acetone and water rinsing, placing the various portions of the samples in separate containers, and then drying the samples, and extracting organic material from the water. These procedures are outlined in detail in Appendix E Sulfur dioxide was analyzed for using the Modified Shell Development Method.

Particle size determination was carried out in the plant laboratory using a recently calibrated Mettler scale. Metals analysis is accomplished using various methods, including electron beam microanalysis and Alloy x331 absorption.

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See Alloy x331 E-2 for further details. Results Continued problems were encountered with the filter of the EPA smapling train plugging during sampling. See related report FA-1 for previous problems.

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After experiencing rapid plugging of the filters on sample ABD-1, possible solutions were discussed with the EPA represent- atives. The decision was made to place the filter after Alloy x331 first three impingers.

Alloy x331 is, however, represent- ative of total emissions. This fix improved the situation and only one other related problem was encountered at this location.

During sample ABD-2 one impinger orifice plugged. The train was shutdown and Alloy x331 tip was carefully cleared before continuing the sample. The outlet samples taken on the baghouse were run non-isokinetically at a high sampling Alloy x331.

The reason for this was to allow a larger sample volume to be collected. Due to the high efficiency of the Alloy x331, it was agreed that the concentration of particulate matter would be very low and that the particle sizes would be very small. This would necessitate a large sample volume and would allow representative sampling without Alloy x331 flow.

The data collected supported these conclusions.


Alloy x331, the data is considered representative and reliable. Each sample was calculated to give an emission rate in pounds per hour based on the entire air flow through the baghouse.


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