Document mqpB9kp6XJ35vaNEpM0epjGjQ
_B. F_. GOODRjCH CH EMI CAL COMPANY TEQHNJ CAL_REPO_RI
TITLE
A VCM Monitoring Downwind From ALGCP
AUTHOR
M. M. 0'Mara
LOCATION
Avon Lake Technical Center
REQUESTED 3Y
See Distribution
SUMMARY
LOCAT'ON
________
DATE
May 16, 1974
pROJEC T NO.
Total Hydrocarbon (OVA) and grab analyses (gas chromatography) were
obtained downwind (240 - 290, 10 - 20mph) from our PVC production facility
at a distance ranging from 0.36 to 0.40 miles. The purpose o-f this analysis
was to establish the normal steady-state concentration of VCM in the atmosphere
at short distances from the plant's boundries.
OVA readings ranged from 50 - 300 ppm while gas chromatographic analyses from VCM ranged from 0.035 to 0.16/.21 ppm.
Analytical studies will continue toward increased sensitivity and specificity.
LOG BOOK REFERENCE!:
DISTRIBUTION:
CTF A. Vittone, Jr. R. D. Scott B. A. DiLiddo J. L Nelson E. W. Harrington E. G. Schwaegerle F. E. Krause
iFc-ieno 4,**m
22929 001
R. N. Rylands R. W. McKay M. D. Rider R. M. Kreager L. A. Bennett A. L. Schultz
CROUP FILE ACO. NO.
D. L. Kent L. B. Crider R. W. Strassburg E. B. Katzenmeyer, Jr. H. Waltemate W. E. Brodine
PRINTED IN J.S
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Page 2 May 16, 1974
Introduction The objective of this initial study was to initiate work on (1) determining
the steady state concentration of vinyl chloride monomer (VCM) downwind from our polymerization facilities and (2) describing the need for additional analytical methods for analyzing VCM below 1 ppm. Our initial approach was to monitor VCM approximately f- mile downwind from the following buildings at ALGCP: 451, 461, 463, and 464.
Location/Method An aerial map of the ALGCP installation is shown in Figure 1. Sampling
locations were along Moore Road and these points are shown on the map ((T), (2), 0, ). The positions chosen were based primarily on the wind direction.
At the time of sampling the wind velocity was 10 - 20 mph (time weighted average = 13 mph)- and at a direction of ~260 (time weighted average direction) .
N 0,360
The deviation in direction ranged from 240 to 290. The 50 cone created by this variance is also shown in Figure 1. Sampling was carried out at various distances along the base (Moore Road) of the cone (the apex of the cone was taken as the center of the four (4) buildings (see Figure 1). Linear distances from the apex of the cone to various points along the base are also shown in Figure 1. These distances range from 0.34 to .40 miles.
Sampling Two methods were employed for sampling the atmosphere. Total hydrocarbon
was obtained by means of the Century OVA portable analyzer. Grab samples for gas chromatographic analyses were obtained at the four (4) points shown in Figure 1. Analyses were performed between 3:45 - 4:15PM, Wednesday, May 15, 1974.
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Page 3 May 16, 1974
Results
The results of the OVA analysis at the time of the grab samples were taken and the gas chromatographic analyses are sunnarized in Table 1. The gas chromatographic analysis ranged from 0.035 to .16/.21 ppm. It is interesting to note that the lowest value was obtained at point 3 which is outside the cone, while the highest value, .16/.21 ppm was ~180 from the time weighted average wind direction (260).
It should be emphasized that the significance of the OVA is highly questionable. At the time that the samples were taken there was a detectable odor that is not characteristic of our plant emissions. The odor was more typical of paint and could be from other industrial sources in Avon Lake. An aromatic solvent from a source of this type will give very high OVA readings since the response in the instrument is about eight (8) times higher than for VCM.
Table 1 Results of Downwind Sampling
Positi'n^3^ 1 2 3 4
Total Kvdrocarbor/k)
55 125
80 70
(a) see Figure 1 (b) OVA readings (c) by gas chromatography
VCM. 0.16, 0.21 0.08 0.035 0.096
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Future Work
While our present chromatographic method is capable of even more sensitivity, I believe a concentrating method is necessary so that the gas chromatographic peaks at these very low concentrations- can be tagged