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Control of Volatile Organic Compounds Emissions from Manufacturing

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averages for the month <strong>of</strong> August 1981. The following are considered<br />

design parameters:<br />

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a)<br />

heat input =2.18 MJ/s (7.45 x lo6 Btu/hr),<br />

,,,,,,,,, 8 88 , , , ,, ,<br />

b) air supply 515.1 standaid m3/s & 'd" (33,900 scfm, at 60O'~)<br />

c) firebox temperature ~980°C average and 1,200°C maximum (1,800<br />

average and 2,200°F maximum),<br />

d) firebox residence time ~1.5 seconds, and<br />

l<br />

l<br />

e) pressure 519 kPa (78 in. H,O).<br />

D.2.1.2<br />

L.<br />

Sampl ing and ~nal ytical Techniques. A secondary purpose<br />

<strong>of</strong> the ARC0 incinerator test was to compare results <strong>of</strong> different<br />

analytical methods for to the measdrement <strong>of</strong> VOC missions. During<br />

the testing phase <strong>of</strong> this program, three differen.t1 methods were used<br />

for the col lection and analysis <strong>of</strong> hydrocarbons. These were:<br />

a) EPA Method 25, 1<br />

b) Proposed EPA ~ethod18 (both on-site and <strong>of</strong>f-site analyses<br />

performed), and<br />

I<br />

c) Byron instruments Model 90 sample collection system and<br />

Model 401 hydrocarbon analyzer sampling system and instrument<br />

combination.<br />

I<br />

To characterize the VOC destruction efficiency across the thermal<br />

Incinerator, liquid, solid, and gas phase samplirig was performed.<br />

sampl ing locations were:<br />

he<br />

a)<br />

~ncin'erator inlet - waste gas stream<br />

- natural gas stream<br />

-atactic waste stream , ,,,,, ,,<br />

,,, ,, ,, , ,<br />

' , ,, , , , ,<br />

, , , 8 ,;; , #, ,, 8 8, 8 , , , ,,<br />

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b) Waste heat boiler outlet, and<br />

c) Scrubber stack out1 et (volumetric flow rate).<br />

I<br />

The sampling system used for Method 25 consmisted <strong>of</strong> a mini-impinger<br />

moisture knockout, a condensate trap, flow control system, and a<br />

sample tank. Both pre- and post-sampling leak tests were performed lo<br />

ensure sample integrity. In the case <strong>of</strong> Method 18, samples were<br />

collected using a modification <strong>of</strong> EPA Method 110 for benzene, This<br />

modification was necessary due to the high moistlare content <strong>of</strong> the<br />

incinerator gases and the positive pressure <strong>of</strong> the emissions. To<br />

ensure that a representative, integrated sample was collected using<br />

the modified Method 18, three val idation tests for sample flow rate<br />

and sample volume into the Tedlar bag were performed.<br />

I<br />

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I

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