------- r~ «° 0 _ V « * •t— Q) •M o 0» c P § 5" £8 < o >» o i; ° S«* 0) O! 0) Q-i X -4-> rtJ O s: o O) LO LO OJ 2: o a> a) *-> -o •p- o oo o ooooooooooooo OLnou-)ouooooir>OLnLn cvioevjo^roor~-^OLoesjOPO CQr—lOOrocvi^rrocO"—'f^-u^ocvj r~-r^-r^Lni—iLOLOCNJcocoPO^rLn OOOOOOOOOOOOO OLnLnoLOOOLnmoLrtLOO '^•mcvjiO'—iroCTii—>ir)«3-ineMO CM^-LOUICO"—•OOLOCOOCVJCMCT^ cNJcnrocsjO'—''—'•—'•—'CvjCMCviesj OOOOOOOOOOOOO LOtnLnoLnLDOoi-rjooLnLn LOCO-^-^roioi^^-LnmCTiiovo '3-voen^totoroCT»ocoirjLno '^CVICMCSJOO^'O^^—«-^-^OSJ OOOOOOOOOOOOO LOLnLnoLnoooi-nirjLomo f\jir>ioo<—i-ervooiLOro^roto cnror^.'o-^r^rvO'a'OOO'—>^rco Op-.-^-^OOOOOrt^-i—.—^ ooooooooooooo uioouiounLOLnooi-nLno i~—<^^Jm^rco^l~c^^CT>lOLno^•^1—i CMQOOOOCMCNJCSJCSJ^^Ln^^f^CTl ooooooooooooo csjLOoomosjoioO'—IOLOTJ-—> OOCMCTli—t-^ r~-CVJCT>CVJOl^O oocorv-cvj^rcdOiomuaor-^CTt iO^OLO»rTS-f--r*«vO'*-^r^r«r Lr>cOLO«a-ocvioocrv'er a'lOOt— •—imLOLnvoro^a-m-^^r ^rm—itvji—ILD — <-oioevjoocoLn mcoa^r-Lncvacvjooon^rLnr^. ooooooooooooo i t i r~-ioe\jur)Ln r-~fnro cr»csj^s-ir>i—i^Dc3^ooocsio^Lf>c\j ouniouor^*x>^i-oO'—"r^f—irocn c\j ^- 10 o CNJ o o 10 ^o r«« f»~ CT> ^^ —«-^^-lr—l^^-I^^OOOOO-^ roooOfnrocO'^O'-^a>r-~oevj •a-mcoCTirooOco^Ocooo«a'*M-^ lor^MLnLrjcomrooocoLfJOcrv r~.r*«CT>c\jiootf>'~'^^'^''*» O^ co -^CVIC\JCVIO^H<—i t-* i—<^^t—, — CVJ a. a. 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"^ AJ.I.H c o 1 1 ------- Figure 6-4 shows monthly overall average concentrations for formaldehyde, acetaldehyde, and acetone at all sites in the 1990 UATMP. Figures 6-5, 6-6, and 6-7 display the monthly arithmetic means by site for the formaldehyde data. Since there is considerable scatter in the total data set, three plots are needed to minimize overlap between individual sites. The overall monthly means are shown on all three plots (Figures 6-5, 6-6, and 6-7) and are displayed using the box symbol. The formaldehyde plots show a considerable variability between sites; however, some patterns do emerge. For instance, most sites show a local minimum concentration in May, and a local maximum concentration in October. In most cases these are absolute minima and maxima as well. Most sites also tend to reach another local minima in September. Since one pair of sites is located in the same city, some additional comments about Figure 6-7 may be made. The two Washington, DC sites, W1DC and W2DC, track rather closely throughout the year, although some months show some separation. Thus, a measure of verification is provided for this city. Figures 6-8, 6-9, and 6-10 display the monthly arithmetic means by site for the acetaldehyde data. The acetaldehyde plots show a bit more variability between sites than the formaldehyde data. However, there is a tendency for local minima in May and local maxima in August. As with formaldehyde, these are usually absolute minima and maxima as well. Other local maxima and minima occur more frequently and sporadically than with the formaldehyde data. The two Washington sites track closely from month-to-month. Figures 6-11, 6-12, and 6-13 display the monthly arithmetic means by site for the acetone data. Acetone maxima and minima usually occur in different months. One difference between acetone and the other two compounds is for a local, and usually absolute, maximum concentration in October. The local maximum found in March for acetone is similar to the local maxima found in May for acetaldehyde. The trends generalized from monthly plots of arithmetic means may or may not be representative of a typical year. However, it does appear that the time of year as described by month plays a fairly important role in influencing carbonyl concentrations, as shown by the differences in the monthly means in the plots. Also, carbonyl concentrations appear to be site specific as demonstrated by the differences between sites in the plots. :aroonvi 1990 Final Heoort 6-14------- 03 i c O o "o _0) o CO CO. CD C O •4-^ 03 O * 0) •a 0) Is a o 03 •a >. CD 2 cc O c/3 c 2? c CD O C O O c O CD C O -*-* CD O CO CD" T3 >. CD o CD CD P CXJ E o u. CO CD 5 O) LL (Aqdd) uoiiejjuaouoo Xigjuom------- 03 Cj± o< 0) 03 E o LL o CD H 0) OJ 03 o5 en 0) OT Z ^ O ex g O en _03 GO •a CD *•••» o .22 CD CO o O5 C as c o c ,0 03 "c O) o c o o CD •a (D 2 ca E o u. tri i ------- u_ LU CL cr < O co H O) 2 co 03 < Q- I OJ a a o 5 i (n 03 CO T3 03 CJ _03 03 CO 5 o 2 C ra c o .0 2 c 03 O c o O 03 •a >, -C 03 2 03 O CO I CO 03 3 O) (Aqdd) uoasJiuaouoo Amjuoui 3-17------- 03 CD 05 CD 03 £ o LL u LOJ i Q > o u O Q. • O C/3 o Q O UQ- < OJ 55 q ci q cd q cd q cj q d CO Q.. mmJ O O i CO T3 03 "o _g 03 03 O O5 05 C .0 .2 ra c o c .g 5 "c 03 O C o o 03 T3 03 ]g 03 E o CO 03 i_ Z3 CD (Aqdd) uoi}E4U83UO3 AIMIUOLU 6-18------- • ------- 03 0< 0) 35 CO -t— » CD O o - 0) Q O o 'O CO ! < Q_ t c Q C 13 . C_ < (T! S < O CO H O) 03 w—• CD ^ CO .i X CO f- ___ ^y < Q- CM 9- o.> JZ CD 2 03 .+•* CD O o 1 CO CD 3 O) u_ 5-20------- u Q ------- o 5 ! CO -a "a ~a5 C/3 O cn c .0 Ta c o c 03 u c o o (Aqdd) uoi;BJiuaouoo------- LU Q. CC < O CO H ------- g '•+— • eg 'u. 03 >CL Oo *> °> -^ CD CD "" C O O O ! O r- <° fa a. \-(0 en -3 .c O • 3 -3 q cd I o ------- 6.5 INTERCARBONYL CORRELATIONS Table 6-8 lists the product-moment correlations and the covariances between the mean concentrations of formaldehyde, acetaldehyde, and acetone for each site and over all sites for Case 1. Differences between Case 1 and Case 2 were minimal, so only Case 1 results are shown. Formaldehyde and acetaldehyde appear more highly correlated than either formaldehyde and acetone or acetaldehyde and acetone. Figure 6-14 shows the correlation between formaldehyde and acetaldehyde concentrations, while Figure 6-15 shows the correlation between formaldehyde and acetone concentrations. Figure 6-16 shows the acetaldehyde-acetone concentration correlation. The correlation coefficient for the formaldehyde- acetaldehyde concentration data is 0.8026, whereas for the formaldehyde- acetone data the correlation coefficient is 0.6154. The correlation coefficienct for acetaldehyde-acetone is 0.6262. The line drawn in each graph locates the regression line. The data used for Figures 6-14 and 6-15 include each analysis, i.e., for Cartridge 1 and Cartridge 2, for each sampling episode in which the paired data was available. 6.6 PRECISION AND PERCENT DIFFERENCES Tables 6-9, 6-10, and 6-11 list the summary statistics by site and over all sites for the absolute percent difference of the cartridge concentration data. Since the absolute percent difference was calculated only when both cartridge concentrations were above the ADL, only results from Case 1 are shown. The absolute percent DIF, a measure of variability, is defined as the absolute value of the difference between the two cartridge concentrations, divided by the arithmetic average of the two cartridge concentrations, times 100: Absolute percent DIF = ABS (X2 - X1)/((X2 + X^/2) x 100 where: ABS indicates the absolute value; X1 = concentration from cartridge 1; and X2 = concentration from cartridge 2. Precision was estimated from absolute percent difference of duplicate sample analysis. For formaldehyde the absolute percent difference averaged 11.5; for acetaldehyde 13.4; and for acetone 15.1. The maximum of any of the percent differences derived from the pairs of cartridge concentrations was 50% or less for six formaldehyde sites, five acetaldehyde sites, and five acetone sites. The maximum percent difference :52 ------- Table 6-8. Correlations and Covariances between the Mean Concentrations of Formaldehyde, Acetaldehyde, and Acetone: Case 1 Site Code All BRLA C4IL CANJ H1TX ORLF PEFL PNTX SAIL TLOH W10C W1KS W2DC Forma Idehyde Versus Acetaldehvde N 306 15 28 30 16 23 35 24 28 17 20 30 30 COR 0.82638 0.91412 0.90786 0.93666 0.55268 0.98519 0.77771 0.58494 0.60528 0.64832 0.87136 0.78469 0.70878 2 3 1 2 0 11 0 1 0 0 1 1 ccv .83654 .16649 .54879 .20095 .07880 .46774 .88420 .15936 .31060 .47822 .55719 .04340 .31203 0. 0. 0. 0. 0. 0. 3. 3. 0. 0 2 j rormaldenyde Versus icetone CGR 66230 79995 23300 80866 15675 .95185 .88159 .57568 .22698 .42833 .71960 .55066 .63309 2. 3. * 0. 2. * 0. 13. 3. 0. * 0. * 0. ]_ D. 2. COV 80683 05467 85293 02693 01942 01520 74795 65079 19817 41705 27112 95689 C2454 0. 0. 0. 0. 0. 0 0 0 0 0 0 •T •J 0 Acetaldehyde Versus Acetone COR .63277 87969 ,26732 * .81455 .30547 * .93896 .83395 .39901 * .20666 * .42720 * .67158 .52521 .81927 COV 0.96399 2.45119 0.34504 0.86696 0.02188 3.59100 0.67919 0.30536 0.04476 0.19560 0.35190 0.33775 0.93115 'Indicates correlation not significant at the 957. confidence level. :52-04S/carUOSf Cjroonvi 1990 Final Reoort 6-26------- 0) o O CD T3 O o en (D 03 £ O LL LO OJ o CM Aqdd 'uoi;Bj;uaouoo 6-27------- .05 CD O O O "o < OlD <0 CD 03 E un OJ o OJ LO O Aqdd 'uo!;ej;u3ouoo 6-28 I in in 'CO o CO IT) ------- £ o CD Q- §? CD 05 Q 03 •4—* CD O Aqdd 6-29------- Site Table 6-9. Summary of Formaldehyde Precision Statistics' Variable Absolute Percent Difference, ppbv Mean Std Dev Minimum Maximum BRLA C4IL CANJ H1TX ORFL PEFL PNTX SAIL TLOH W1DC W1KS W2DC Formaldehyde Formaldehyde Formaldehyde Formaldehyde Formaldehyde Formaldehyde Formaldehyde Formaldehyde Formaldehyde Formaldehyde Formaldehyde Formaldehyde 30 28 30 26 27 41 29 29 22 30 30 30 9.086 8.334 4.584 8.499 5.669 8.295 30.746 15.991 12.011 14.491 4.570 16.576 12.033 7.333 5.268 7.714 8.662 9.331 33.318 32.788 14.372 19.549 4.673 19.848 0.152 0.409 0.000 0.608 0.426 0.000 0.530 0.138 0.289 0.000 0.137 0.900 55.200 31.606 24.633 34.043 46.099 43.956 115.542 150.127 66.035 70.185 21.074 69.457 In Case 1, mean concentrations are calculated using detectable cartridge concentrations only. :32-045/can.208f ^jrDonvi 1990 Final fieoorr 6-30------- Table 6-10. Summary of Acetaldehyde Precision Statistics5 Absolute Percent Difference, ppbv Site Variable N Mean Std Dev Minimum Maximum ALL BRLA C4IL CANJ H1TX ORFL PEFL PNTX SAIL TLOH W1DC W1KS W2DC Acetaldehyde Acetaldehyde Acetaldehyde Acetaldehyde Acetaldehyde Acetaldehyde Acetaldehyde Acetaldehyde Acetaldehyde Acetaldehyde Acetaldehyde Acetaldehyde Acetaldehyde 319 21 28 30 21 24 36 29 27 14 30 29 30 13.437 12.031 11.260 6.603 14.961 15.040 11.867 12.148 11.957 30.348 15.797 10.864 17.635 16.683 12.049 15.539 5.009 18.307 24.044 10.313 9.319 12.285 28.454 18.520 12.231 24.101 0.000 0.000 0.000 0.344 0.000 0.743 0.000 0.000 0.000 1.905 0.000 0.374 0.000 101.967 42.105 54.035 18.911 61.538 101.967 48.819 38.095 38.760 75.918 62.774 61.176 84.569 In Case 1, mean concentrations are calculated using detectable cartridqe concentrations only. :52-045/can.208f :i.'Donyi 1990 Final Reoort c -3 i------- Table 6-11. Summary of Acetone Precision Statistics2 .Absolute Percent Difference, ppbv Site Variable N Mean Std Dev Minimum Maximum ALL BRLA C4IL CANJ H1TX ORFL PEFL PNTX SAIL TLOH W1DC W1KS W2DC Acetone Acetone Acetone Acetone Acetone Acetone Acetone Acetone Acetone Acetone Acetone Acetone Acetone 298 15 28 30 16 18 33 20 28 22 30 29 29 15.133 8.903 13.793 9.058 23.399 21.043 13.453 11.393 11.368 12.236 21.966 13.056 23.036 16.469 9.503 16.788 8.755 15.585 20.031 16.152 10.915 11.869 13.908 17.461 18.194 22.876 0.000 0.289 0.000 0.000 1.575 4.831 0.000 1.690 0.000 0.468 1.000 0.000 0.000 99.728 36.190 69.630 40.528 48.837 93.878 70.487 43.478 35.514 68.599 65.185 55.556 99.728 In Case 1, mean concentrations are calculated using detectable cartridge concentrations only. :52-045/can.20Sf Cjroonyl 1990 Final fleoort 6 - 3 2------- was larger than 100% for only two formaldehyde sites and two acetaldehyde sites. The largest percent difference for any of the acetone sites was less than 100 percent. These results show good precision, and speak well for the sampling and analytical procedures. These results are in agreement with the 1989 results, indicating consistency between the two years in terms of precision. 6.7 AUDIT SAMPLES Table 6-12 displays the results from the audit samples for formaldehyde, acetaldehyde, and acetone. Figures 6-17 and 6-18 display bar charts for the percent differences between the spiked and reported samples for formaldehyde, acetaldehyde, and acetone. An overall negative bias is evident for all three compounds in both Table 6-12 and Figures 6-17 and 6-18. This overall negative bias-was over four times as much for acetaldehyde as it was for formaldehyde. The bias for acetone was about the same as it was for formaldehyde. There was an evident trend in the audit results. The audit results are illustrated graphically in two separate graphs. Figure 6-17 presents audit data analyzed prior to instrument system maintenance. After the analytical system maintenance, the audit results improved as indicated in Figure 6-18. The audit results over the course of the program indicate that the analytical system was in control and the analytical results valid. :52-045/can 2CSf :.srBcmvi 1990 Final Reoon 6-33------- Table 6-12. Spiked Quality Assurance Cartridge Results for 1990 UATMP Monitoring Sample Number A4 A7 A 12 A15 A16 B7 Bll B14 1 C7 C14 C16 • C20 i D3 ! D7 D15 D17 D19 A3 A9 A17 B3 B9 B15 B16 Formaldehyde j Acetaldehvde Acetnr,« i Spiked (ppbv) 1.01 1.01 1.01 1.01 1.01 2.01 2.01 2.01 2.97 2.97 2.97 2.97 4.02 4.02 4.02 0 0 1.01 1.01 1.01 0 2.01 2.01 2.01 Reported I (ppbv) 1 1.13 0.87 0.85 0.85 0.80 1.79 1.82 1.75 2.60 2.52 Percent j Spiked Difference i (ppbv) Reported I Percent Spiked 1 Reported 1 Percent (ppbv) 1 Difference i (ppbv) 1 (ppbv) Difference I 10.62 1 0 1 -999 ! 0.00 1 3.02 I 2.55 1 -18.43 1 -16.09 -18.82 -18.82 -26.25 | -12.29 -10.44 -14.86 -14.23 -17.86 3.04 I 2.30 1.02 j -999 1 100.00 1 3.02 i 4.04 i 25.25 1 1.02 1.02 1.02 2.00 2.00 2.00 2.00 1.27 i 19.69 j 3.02 | 2.35 i 0.72 j -41.67 0.94 1.73 1.99 1.62 1.53 2.00 | 1.57 -8.51 -15.61 -0.50 -23.46 3.02 j 2.54 3.02 4.02 4.02 4.02 -30.72 i 3.02 -27.39 | 3.02 2.00 2.00 1 0.00 1 3.02 2.54 3.84 4.64 3.69 2.71 2.78 1 -28.51 -18.90 -18.90 -4.69 13.36 -8.94 -11.44 -8.63 2.47 -22.27 2.69 i -10.41 i 2.00 i 1.58 1 -26.58 1 3.02 1 -999 100.00 i 4.20 3.56 3.83 -999 -999 0.96 0.88 0.94 -999 L.72 2.04 1.89 C3 ; 2.97 j 2.64 CIO CIS C24 D9 D16 D20 AS All A18 A19 BIO B17 B20 C9 C12 ! C13 2.97 2.97 0 4.02 4.02 0 1.01 1.01 1.01 1.01 2.01 2.01 2.01 2.97 2.97 4.29 -12.92 -4.96 0.00 0.00 -5.21 -14.77 -7.45 0.00 -16.86 1.47 -6.35 0 3.96 3.96 3.96 3.96 0 1.02 -999 I . 0.00 | 2.00 I 2.06 i 2.91 3.78 ) -4.76 2.00 1 1.48 -35.14 3.92 3.66 4.03 -999 0.88 1.02 | 0.84 2.00 i 1.50 -1.02 -8.20 1.74 0.00 -15.91 -21.43 -33.33 2.00 i 2.06 1 2.91 2.00 j 1.89 -5.82 2.00 1.75 i -14.29 2.00 2.00 2.00 3.02 3.02 0 4.02 4.02 4.02 1.42 | -40.85 2.04 | 1.96 1.60 3.01 2.61 -999 2.62 4.89 3.56 4.02 ! 4.26 -12.50 1 0 -999 1 0.00 1 3.02 ! 1.62 2.94 | -1.02 | 2.00 1 2.00 1 0.00 1 3.02 1 2.35 2.92 -999 4.00 2.77 -999 0.95 1.02 1.02 0.97 1.90 2.03 2.01 3.08 2.92 -1.71 0.00 -0.50 -45.13 0.00 -6.32 0.98 0.98 -4.12 -5.79 0.99 0.00 3.57 j -1.71 2.00 0 3.96 3.96 3.96 1.02 1.02 1.02 1.02 2.00 2.00 2.00 2.00 2.00 2.97 1 2.87 1 -3.48 i 2.00 1.79 -999 3.66 3.40 3.76 -11.73 0.00 -8.20 -16.47 -5.32 1.00 i -2.00 1.31 1.17 1.14 2.20 2.19 22.14 12.82 10.53 9.09 1 8.68 2.08 1 3.85 2.14 | 6.54 2.14 I 6.54 -25.00 -0.33 -15.71 0.00 -53.44 17.79 -12.92 5.63 | -15.27 j -28.51 3.02 | 2.69 I -12.27 0 | -999 2.00 i 1.71 2.00 2.00 3.02 3.02 0 0 4.02 0 0 3.02 1.55 1.75 2.90 3. 14 -999 -999 3.97 -999 -999 3.34 3.02 ! 3.06 0.00 -16.96 -29.03 -14.29 -4.14 3.82 0.00 0.00 -1.26 0.00 0.00 9.58 i 1.31 2.03 i 1.48 i 3.02 1 3.05 i 0.98 6-34------- Table 6-12. Spiked Quality Assurance Cartridge Results for 1990 UATMP Monitoring Sample Number CIS C23 018 D23 A10. A13 A14 A20 A24 r^ A B4 B8 B12 B13 Big B19 C4 C8 /"^ 1 1 Cll C17 C19 ^\ it D4 T*\O O8 DIO Dll PV 1 ^ U12 D13 D14 111 .a — Formaldehyde i Acetaidehvde Acetone Spiked (ppbv) 2.97 0 0 0 1.01 1.01 1.01 1.01 0 0 2.01 2.01 2.01 2.01 2.01 2.97 2.97 2.97 2.97 2.97 4.02 4.02 4.02 4.02 4.02 4.02 4.02 i -*i Reported (ppbv) 2.90 -999 -999 -999 0.99 0.92 0.97 1.00 -999 -999 2.01 Percent ! Spiked Difference 1 (ppbv) -2.41 0.00 0.00 0.00 -2.02 -9.78 -4.12 -1.00 0.00 0.00 0.00 2.08 | 3.37 1.96 2.11 1.94 2.93 3.05 2.96 2.95 2.97 3.97 4.03 4.06 3.76 3.92 4.09 3.87 — i -2.55 4.74 -3.61 -1.37 2.62 -0.34 -0.68 0.00 -1.26 0.25 0.99 -6.91 -2.55 1.71 -3.88 2.00 0 3.96 0 1.02 1.02 1.02 1.02 0 2.00 2.00 2.00 2.00 2.00 2.00 0 2.00 2.00 2.00 2.00 0 3.96 3.96 3.96 3.96 3.96 3.96 Reported (ppbv) 2.11 -999 4.12 -999 1.16 0.96 1.09 0.97 -999 2.03 2.03 1 Percent Spiked 1 Reported Difference I (ppbv) i (ppbv) 1 5.21 t Percent Difference 1 0 | -999 1 0.00 0.00 | 0 i -999 3.88 i 2.00 0.00 12.07 -6.25 6.42 1.92 0 I -999 3.02 i 3.04 3.02 3.02 -5.15 i 0 2.96 2.90 -999 0.00 i 0 ( -999 1.48 i 4.02 4.04 1.48 i 4.02 1 3.96 2.10 | 4.76 1 4.02 1 4.02 2.10 | 4.76 2.07 1.91 -999 1.92 2.00 2.13 2.01 -999 4.08 4.00 3.38 -4.71- 0.00 -4.17 0.00 6.10 0.50 0.00 2.94 1.00 4.02 1 3.97 0 0 3.02 3.02 3.02 0 0 2.00 2.00 2.00 -999 -999 2.99 2.89 3.04 -999 -999 1.94 1.98 1.97 4.00 i 1.00 1 2.00 1 1.92 3.95 4.01 3.95 -0.25 1 2.00 1 1.94 1 1.25 I 2.00 | 2.02 -0.25 i 2.00 0.00 -4.17 0.00 0.66 -2.03 -4.14 0.00 0.00 0.50 -1.52 i 0.00 -1.26 0.00 0.00 -1.00 -4.50 0.66 0.00 0.00 -3.09 -1. 01 -1.52 -4.17 -3.09 0 00 I 1.96 i -2.04 i ^!Z!! •*« -1.20 .4.32! '-999" indicates concentration below analytical detection limit (ADL). 6-35------- CO •4—* D CO CD DC Quality Assurance 1990UA 6-36------- CO ^""> mmmUi 13 CO CD DC H—» T3 -^ ^CL <, ^ 1 h-£o 2 8 _ CO _J -y— CO CO _>* 15 13 i i ' i i i i t i i 1 1 i j • 1 T i i m mm c d5 •• ; mmm ; i ! ' * 1 i i i - ! ! I i 1 i i i I | - 1 — 1 i i " 1 j ^HM i i i — i r mmmmt i i ! i i i i i ; 3 3 =1 3 =s 3 1 3 , ml : : J, 3 3 r- g = 3 = = =3 ! i ^3 I ! i 1 j ] ' 1 1 ( ! 1 ' . 1 1 [ i I 1 j 1 T 5 ~ n _5 OJ _5 _Q o a s s "~d> o f^ _0 _o CO O ^ o ~"o> _3 9 m ~co -S fc -;-S -s E S =5 ~*Z -p 03 2 "5. 1 E ~n O3 -| ^ < :1 a ~"n cy _O 3 -i _o (N _o en O ~S _CD N. ffi O CO ~3> < CO . _< _< CO < 03 2 "03 < 1 — 03 •a *^lh ^^ JZ 03 2 CO "53 O < 1 03 •a >, JZ 03 T3 03 O LL. O5 ' O5 ^f CM a. < i T— O 03 ^ CO k_! 03 ^ co~ «-^ i_J CO 03 QC •^—t '•a 2 < CD o C 03 u_ 3 CO CO < •^ J*^ "03 3 a CO 1 CO CD 3 Ol LL 6-37 ------- 7.0 CONCLUSIONS Based on the discussion in the data analysis section, the following conclusions were reached: 1) The mean concentration data for all three compounds are more nearly lognormally than normally distributed. 2) Mean concentrations varied from month-to-month for all three compounds, but the variation of acetone concentrations was somewhat different than the variation of formaldehyde or acetaldehyde concentrations. This variation did not appear to be represented by regular cycles. In addition, the monthly concentrations also appeared to be site specific, particularly for acetaldehyde. Analysis of variance results indicated that both site and month played a role in influencing mean concentrations for all three compounds; however, other unknown factors appear to have an even greater influence. 3) Formaldehyde concentrations were fairly highly correlated with acetaldehyde concentrations at all sites. However, neither formaldehyde nor acetaldehyde concentrations were well correlated with acetone concentrations. In fact, the correlation coefficients of formaldehyde and acetaldehyde concentrations with acetone concentrations were non-significant at some sites. 4) Absolute percent differences and audit samples biases revealed that the sampling and analytical methodology employed is repeatable and valid. 5) The use of a denuder in the sample collection system was determined to remove > 99.9% of the ozone. Therefore, the formaldehyde results reported here are not negatively biased by the ozone present in ambient air. :=2O45/can.20Sf "araonyl 1990 Final Recoct 7-1------- 8.0 REFERENCES 1. McAllister, Robert A., Emily G. Bowles, Judith DeGarmo, Joann Rice, Kobert F. Jongleux, Raymond G. Merrill, Jr. and Joan Bursey, "1990 Urban Air Toxics Monitoring Program" Draft Final Report prepared for Neil J Berg, Jr., U.S. Environmental Protection Agency, Research Iriangle Park, NC, Radian Corporation DCN: 91-262-045-55, Research Triangle Park, NC, June 1991. 2. McAllister, Robert A., Phyllis L. O'Hara, Dave-Paul Dayton, John E. Robbins, Robert F. Jongleux, Raymond G. Merrill, Jr., Joann Rice, and Joan T. Bursey, "1990 Nonmethane Organic Compound and ihree-Hour Air Toxics Monitoring Program," Final Report, prepared for Neil J Berg, Jr.; U.S. Environmental Protection Agency, Research hnangle Park, NC, Radian Corporation DCN: 91-262-045-04, Research Triangle Park, NC, January 16, 1991. 3- Merrill, Jr., Raymond G., Dave-Paul Dayton, Phyllis L. O'Hara, and K. F. Jongleux, "Effects of Ozone Removal ont he Measurement of Carbonyl Compounds in Ambient Air," 84th Annual Meeting and Exhibition. Air & Waste Management Association, Vancouver, British Columbia, Canada, 4. SAS® Institute Inc., "SAS® Procedures Guide, Release 6.03 Edition " Cary, NC (1988). 5. Aitchinson, J. and J. A. C. Brown, "The Lognormal Distribution," Cambridge at the University Press (1957). 252-045/can.20af Carbonyi 1990 Final Renort g _ 1------- Appendix A - Site Information from AIRS :52-045/can.203f :arnonyt 1990 Final Reoort------- Table A-l 1990 Urban Air Toxics Monitoring Program Sites EPA Radian AIRS Region City Site Code Number II Camden, NJ CANJ 34-007-0003 III Washington, DC W1DC 11-001-0025 Washington, DC W2DC 11-001-0039 IV Orlando, FL ORFL 12-095-2002 Pensacola, FL PEFL 12-033-0004 V Chicago, IL C4IL 17-031-0060 Sauget, IL SAIL 17-163-1010 Toledo, OH TLOH 39-095-0081 VI Houston, TX H1TX 48-201-1034 Baton Rouge, LA BRLA 22-033-0006 Port Neches, TX PNTX 48-245-4007 VII Wichita, KS W1KS 20-173-0010 :62-045/can 208f C^roonvi 1990 Final Report------- -j Q 01 (O UJ (- V > £!2S §"§ S -J cc |sa gag Z X Q u<£ £ to .u O X h- 5: UJ (_J OJ cTi a. 5 < ZJ o NM1SV3 WJ - •z. CM O) ^ oi CM JJ Q ^ P <: tn 1 t— a" T ai 03 .n >- t— a r^. o ^ in CM 03 «r Q 7S O u_ LL_ Q $ S r^ in en en -^ S (5 2 O Q u JEFFERSON --. rr CM > h- Q CJ ^< GH n" 5 <, ^ L? ^. U OJ > O -^ ^ EVATION t -i UJ iT) UJ § ri 5 < z. < LO q SOUTHERN I 3 o I H O < 33 ^3 .n CM Ol n" 2 O 5 ^ | B < t/> P SOUTHEAST a a. f— CORD LA£ LU CC 1 r*. f^ m C3 Z ~ O z 5 HESIDENTIAI aj i/i a z 2 Q X S << LO LU ^U < < ^ LU O s 1— (/) 5 UJ < _j § UJ a SUBURBAN CM C3 [3 uJ Ul O !— < y 2 o UJ < 2 ^ ^ UJ t— UJ < O g u MPASS S£ O u > a 'jj 0 2 i— ai O X H- (/J* UJ y z i z <£ 2 UJ in CM _r r o •r> g ^ t/j > g C3 Lrt LU 0 LU 2 X £ U) '_0 UJ cc < aj j5 :T DATA UJ Q Z u < cc < 2 < m >— 2 0 < UJ CQ ;- S S, < tn 2 a a: g 03 O a: O u X LO 5 UJ h— > O 2 LU O < O 2 | In x' I cc < ^ X £------- EASTING 2 z 8 C3 u. LL 5 S 8 .a LU O 33 < O t— < > LU LU s ~ RDIAST O CJ OJ £ REQ EVA h- CO CC 1 'ASS SEC Q O < K < *— UJ < o u < f 2 s •= ° = i s < o t < a > 1 Z I/) Si [RIC INFOHMATK AIR QUALITY LU 2 o cc UJ < < a. LU •z SITE DESCRIPB Q Z g u. CN" LU h- < t— CO CANTONMENT; ESCAMBIA CO O o MOBILE-PENSA CO PAMAMA CITY INDUSTRIAL SUBIIFIBAN CN 0 •z. _ a \— UO aJ T ~ — i/l Si - B .u 2 — > S So > i ? § ^ § *z o a < o o u u < -j _- cc S ? 3 ION I I1 p Lo CL LU 5 LU>(_, uTCCLUmcT ^ ir±O <U •z. ITING AGE s. ~ — Q a! s±. i — Q Z. UJ 2 X O Q Q ^_ I o o ------- *r 'M m CD 2 UIMEASTI z m S3 in 33 r*i m o (U u_ u_ Q 5 CM CM O K! N- O) _J •SI ^ s O 2 < ELEVATION> iss §sg g£f Ii* 12S 0 1— o < z 1 I o z X tn I 0. < u _J < § < z _ i < o X UJ 2 i o tU u Q Z < Z < Z) X 3 £ O TMP SITE CODE: W1DC < 001-0025 CITY (00000) 1 COUNTY (001 ' ITEID IFY POPIIIAHON ^ u h- T O_ X 8 < r*1 Ol f*« U9 LO o> c^' OCR POPULATION < LAND USE i;, ATE ESTABLISHED . Q LOCATION St ATE TERMINATED . Q COMA SC PINEY BRANCH ROAD & DAHLIA ST N j_ TE ADDRESS u-> SHINGTON. DC-MD-VA 1 RBAN AREA (Ua<10) . 3 'IRONMENTAL CONTROL DIV . D C DCRA ON ROOh Of- GYMNASIUM BLDG. 03 MONI 1 OH If z £ LU h- JPPORTING AGENCY 01) 3MMENIS : s a a m 0 LU I— < Q X < e— ------- s ^ 3. T (71 n a z 5 < s s S i UJ U 2 Jt 5 a z <; o -1 O U I O < Q (jo 03 n = Q 35 2 Z X o o IN Z <2§ 31 O U a x Q T 5 i«! M S££ S 5 5 S 5 O Q CV( g LU 8 U IATMPSITI a < z i— o z 2 g > G Ol COO-LOO It Q UJ jl e a i Ol 1 > H z - NOIIVH CIIYPOPI o _i 1 h- < z ;T X 8 < m 01 ^ s a> fN 3^ 'ULATIOI 2 CC 8 < g LU 2 O o ^j LU 01 D Q 1 Q ABLISHE DATE EST LOCATION SE'IIING (1) . URBAN AND CITY O MINATE CC UJ h— UJ < Q )AD AVE S E WASHINGTON D C w 2I50RAILR Ol Ol UJ SHE ADDI 5 a a WASHINGT 5" •r § i URBAN AF NTAL CONTROL DIV . D C DCHA UJ ENVIRONM >- NGAGE SUPPORTI (1)01) FIOF'EHTY DIVISION WAREHOUSE NEXI IO ROUTE 1 29b UJ o £ o Q 01 COMMLNI COD SCAIE LEAD MONITORING SITE SAMPLING BEGUN Ob 01 S3 ~T NOGHBOftt O LU t/1 LU Cl------- o 2 U1 5 5 Z) z f) -N tn kO s 2 o u_ u. o S S iri p m rs. _li •*r TT _j < •> LA5T REQ E' (0 t 5 Q h- O UJ COMPASS S f^ o o MET DATA > < £ LU Q <; ct -i z s. 5 _LJ >— -T t/) < LU CC t X z o THIC INFORMATI 2 P cn > 01 03 3 U) AIR QUALITY > x 0 h- z S — Z o SITE DESCRIPTI > 'jj 01 cc ^ § UJ z ? m LU H < 1— CO TITUOE 3 CAMDEN Q O H- C3 Z o _i CAMDEN CO M ZONE i— 3 -* METROPOUTAr PHILADELPHIA r— CC O z 2 i— 3 RESIDENTIAL a uj -1 U 1! O £ r Q SUBURBAN 3 Q ti3 5 < M 2 Z g HO -^ —' ai 5 3 2 X 5 8 V en a Q a Q UJ :RMINAT »— LU S a. 3 O x" UJ 1 I— z LU Q < CJ DRESS C < —1 z s < z ILADELP I 0. f .0. < cc < z < 2 LU a UJ 1 — < -^ > W JERSf LU Z > O z UJ TING AG £ s ^ ,- S SI 5 ~ 2 Z a _j ^ So 6 * =,- 5 1- " 2 S s "" ~- < 7) < o •" ^ ^: % a a. STA X L^J < < ^ X i; S ^ Q ji z: ^ ^.------- o T "J U[M EASril s o LL. u. 5 5 aj S 2 ELEVATION =^ 1 T UPDATtD . fn RECORD LA: LU a LU X 3 LU COMI'ASS S - MET DATA Z g S g 01 LO O a < u O 2 r o * 5 ~> '2^2 ^2 x en uj O ,- >- > z. uj en 2 ~ O^Q _ *- t t ^ Hi I 2 = " ^ o o CITY ( COUN X Q < a | 8 o < z o 5 z o •- " in N-" o O a m - y_ U ^ PULATIOI £ Q < a TABLISHE m UJ UJ t- < G Q RMINAIE UJ i— UJ ^ O t/) CO E < LU t— to P 3 UJ CC Z m cc 2 > u z ING AGE ^ L?~ c_ i~ — 2 «T ti. VT JJ ^ S O u t Z -J 11------- CO O S 5 (3 — UTM EASl z m UTJ m 03 m CD LU U_ Q $ en T g § 3 < — ELEVATIOI un i — (/) < RECORD 1 , rsj in fs» rvj *r —i < > UJ 1.AST REGu z SUPPORTING AGE (001) J") Z* ^ o CJ O X LU t/> D LU J^ ------- 3 n "^ <. 2 i _ z i/) s 5 G U_ Q 01 & < g f— < > LU UJ IPDATED 01 <5 O c O CJ LU X ^ > LU 0 LU X h- ol < o ^ LU ol CO (/) < o u < § 1— LU CM Ol »- <2§ S^s X CO UJ fc S z 01 3 LU i- § t i- O S § o ^ - o o z a £ X Q O «g------- a 2 2 5 S a § S 3 Q I O O Q LU z 3 s s? 2 § 5£ a: to S «? X CD §3 II So 2 Z y * a: i- LU O cc UJ < < CO ^ i LU 8 u LU IATMP SI : 201730010 CITY (79000) . WICHITA IATITUUE ' 279.835 COUNTY (17j, SEDGWICKCO LONGITUfjL• -* 3 N : 602.705 AQCH (099) SOUTH CENTRAL UTM ZONE KANSAS -D • LANDUbE(l) RESIDENTIAL UTMNOHIHI O JPULATI tf X y < lAUMbl j~i -U -U < D " LOCATION SL 1 IING (1) URBAN AND CENTER HO EVAI. DA] arv HELATH DEFT . 1900 EAST 9TH ST DISTANCE Cl HMINAT LU Lj < CO I/) LU a < LU iO) . WICHITA. KS HC IMO T J) < UJ < 2 < CD T 21 < L/l 5 5 1 2 UJ a z < < UJ O 2 UJ 5 tr < a UJ to < ;/) 2 2 >- O Z UJ ING AG r— - § : SITE OPERATED BY WICHITA SEDGWICKCO HEALTH LJLPT ^ :OMMLN : AT CITY-COUNTY HEALTH BLDG ACTIVE 1/1/73 H-INI-O UJ ------- _ a z g 5 — = o z X *5 o ^j x 2 * g 2 IIS 2 I < g x o §s§ IP si| z cc a 3<* X "1 h- aj 2 O X < 2 U_ ^7 UJ t— iji EHPAHK j— 2 O O s z < X o s X o U- ! t— z UJ u /lERCIAL f^ o o ^ N ANDCtI < x 3 P C3 Z h— a 03 5 x < < -U LL ^3 <4 i § CD CD . 01 m to O r> n Q J ~ 5 "- 5 03 O O 01 Q UJ |ll 5 O O I S O O 5 2 z z UJ UJ UJ UJ g g x o z o 3 5 ^ < o 5 uj >~ < i ~ ^ T------- a 2 O ° I u- > < s o I— u a <" LU U} CC < 2 3 J z a _n z o i^ 1 I a £, _ u 5 1 UJ i- ±r < a "^ o ^° r a r 2 o Q SUBURBA ^ 2 X Q t 3 8 I a u < 5 2 O 8 s O X (/) cr > LU 5 S ^ 2 in O) a O) n 354.635 713.772 71/06/01 a. a. r FRIENDS 2 x o TOLEDO. Q LU _J S. CITY OF : "z I)J ENVIRON m LX LU m SO2 BUBf S S g LU j5 TY POPUIATION u jCR POPULATION < UE ESTABLISHEI Q UE TEHMINAFEC t*. IE ADDRESS (/) IBAN AREA (b-l(JC 3 !PPORTING AGEN 15) MMENlb 3 S. Z o ~L. 2 CC LU LO a UJ ./)------- 2i o SCSJ -^ CO 01 i/i 5 g 2 « 5 2 t S ~ u, h- _ _ jj «r 3 Q UJ X J Jq uj - O i x O h- z g o ij - Z 3 H o SIS s •*; p — < x a S i § a uj ^ £ < •- Q ^2 cj ul X I/) o «> O Z I ' u• x b 3 0 X ca iO a. 3 a a uj 2 s >- = S o z o 3 < z s 2203301 g UJ h- Co 219.419 z g 3 p > »— u 1 CN CT m" z AODH POPULATIC CO/10/06 : Q UJ DATE ESTABUSI- s DAtE TERMINAT a | UJ 9 !/} X UJ 1600 RIVI SHE ADDRESS 5 LU CD 3 1- < CD o" -S URBAN AREA (U/ STATE DLPARIMENTOI < LoulSlA^ > z 01 SIIPPOHTING AG (001) E HEl OCA! ION FOR 2'< •f> CAPITOL COMMLNIS SITEUSEH-INPO ------- Appendix B - Summary Statistics for Cases 1 and 2 for All Sites :S2-045/can.208f Zaroonvi 1990 Final Reoort------- TABLE B-l. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE I1 Baton Rouge, LA (BRLA) Sample Data 10-Jul-90 16-Jul-90 22-Jul-90 28-Jul-90 03-Aug-90 09-Aug-90 15-Aug-90 21-Aug-90 27-Aug-90 02-Sep-90 08-Sep-90 14-Sep-90 20-Sep-90 26-Sep-90 02-Oct-90 08-Oct-90 14-Oct-90 20-Oct-90 26-Oct-90 Ql-Nov-90 07-NOV-90 19-Nov-90 Ol-Dec-90 13-Dec-90 2S-Dec-90 06-Jan-91 18-Jan-91 30-Jan-9I 12-Feb-91 23-Feb-91 Week Day M Sn St F Th _W_ _L _M_ Sa St F Th W T M Sn St F Th W M St Th T Sn _F_ _W T T 1409 1417 1427 :433D 1445 1447 1453 476D 1493 497D 1512 1534 1556 1562D 1584D 1594 Average ) iber P7 )3 M 17 >1 11 18 VI "8 >5 0 2 4 6 19 7 7 ID 5 7 3 D 3 D 2 4 6 D D 4 ge Formaldehyde Mean2 Cone (ppb) 5.26 4.34 2.50 6.74 4.33 6.13 6.59 6.83 3.60 2.62 2.74 3.72 5.25 10.98 5.43 3.84 6.54 5.63 4.90 6.16 6.51 6.79 4.24 3.72 6.10 2.18 2.80 2.50 6.91 3.95 4.99 Absolute^ Percent Diff 11.41 3.23 55.20 12.76 18.73 2.12 0.15 24.01 21.67 8.80 32.54 8.06 1.72 0.82 2.21 0.78 0.31 7.46 0.41 0.81 1.84 4.27 4.49 6.45 0.98 16.51 1.43 16.43 2.17 4.82 9.09 Std* Dev (Pfb) 0.42 0.10 0.98 0.61 0.57 0.09 0.01 1.16 0.55 0.16 0.63 0.21 0.06 0.06 0.08 0.02 0.01 0.30 0.01 0.04 0.08 0.21 0.13 0.17 0.04 0.25 0.03 0.29 0.11 0.13 0.25 Acetaidehyde Mean1 Cone (ppb) 1.03 2.08 - - - 2.28 2.30 1.18 - - - - 1.40 7.24 2.22 1.43 3.92 3.20 3.70 3.54 3.18| Absolute3 Percent Diff 7.77 29.40 * * * 14.91 4.79 * * * * * 15.05 2.21 2.70 5.59 0.51 7.50 8.93 0.00 2.52 1 Std> Dev (ppb) 0.06 0.43 * * * 0.24 0.08 * * * * * 0.15 0.11 0.04 0.06 0.01 0.17 0.23 0.00 Acetone Mean2 Cone (ppb) - - - - - 3.38 _ Absolute- Percent Diff * * * * * I 5.92 1 * _ * - 1 * - - - - 7.20 0.82 - 3.46 4.35 2.69 4.88 * * * * 4.03 14.63 * 0.29 8.98 1 StdJ Dev (ppb) * * * * * 0.14 * * » * * * * 0.21 0.08 * 0.01 0.28 1.12 | 0.02 5.95 | 0.21 0.06 ) 3.45 1 1.16 1 0.03 3.96 | 24.75 | 0.69 | 2.95 1 15.59 1.33 - 2.26 1.15 1.30 1.30 3.67 1.74 2.52 42.11 ! 0.40 * 1 * 5.76 | 25.33 | 10.77 33.85 2.46 5.75 1 12.03 0.09 0.21 0.10 0.31 0.06 0.07 0.17 1.05 - 1.36 1.24 1.70 1.60 4.06 1.53 2.86 36.19 « 8.12 | 9.68 1 1.18 18.75 2.71 1.97 i 8.52 0.33 0.27 * 0.08 0.08 0.01 0.21 0.08 0.02 0.13 In Case 1, mean concentration, are calculated using detected rube concentrations only. •-" indicate, concentration below analytical detection limit (ADL). "*• indicate, insufficient data to perform calculation.------- TABLE B-2. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 2' Baton Rouge, LA (BRLA) Sample Date 10-Jul-90 16-Jul-90 22-Jul-90 28-JuI-90 03-Aug-90 Week Day T M Sn St F 09-Aug-90 I Th 15-Aug-90 | W 21-Aug-90 i T 1 27-Aug-90 I M 02-Sep-90 | Sn 08-Sep-90 l4-Sep-90 St F 20-Sep-90 | Th 26-Sep-90 02-Oct-90 08-Oct-90 14-Oct-90 20-Oct-90 26-Oct-90 Ol-Nov-90 07-Nov-90 j 19-Nov-90 W T M Sn St F Th W M Ol-Dec-90 I St 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 12-Feb-91 23-Feb-91 Th T Sn F 1 w F T ID Number 1297 1303 1304 1317 1321 Formaldehyde | Acetaldehyde Mean Cone (ppb) 5.26 4.34 2.50 6.74 4.33 1331 | 6.13 1338 1347 Absolute Percent Diff 11.41 Std Dev (ppb) 0.42 3.23 1 0.10 55.20 0.98 12.76 0.61 18.73 0.57 2.12 0.09 Mean Cone (ppb) 1.03 2.08 0.18 0.18 0.18 2.28 Absolute Percent Diff Std Dev (ppb) 7.77 | 0.06 29.40 | 0.00 0.00 0.00 14.91 0.43 0.00 0.00 0.00 0.24 6.59 | 0.15 0.01 j 2.30 4.79 I 0.08 6.83 I 24.01 1.16) 0.68 147.061 0.71 Acetone | Mean Cone (ppb) 0.18 0.18 0.18 0.18 0.18 3.38 0.18 Absolute Percent Diff 0.00 Std Dev (ppb) 0.00 0.00 | 0.00 0.00 1 0.00 0.00 0.00 0.00 0.00 5.92 0.14 0.00 | 0.00 0.18 | 0.00 | 0.00 1358 j 3.60 1 21.67 0.55 | 0.18 1 0.00 | 0.00 0.18 | 0.00 I 0.00 i 1365 1380 1382 1394 1396 1409 1417 1427 1433D 1445 1447 1453 2.62 I 8.80 0.16 2.74 3.72 5.25 10.98 32.54 1 0.63 8.06 1 0.21 1.72 I 0.06 0.82 5.43 | 2.21 3.84 6.54 5.63 4.90 6.16 6.51 0.78 0.31 7.46 0.06 0.08 0.02 0.01 0.30 0.41 0.01 0.18 | 0.00 1 0.00 | 0.18 | 0.00 1 0.00 | 0.18 0.18 1.40 7.24 2.22 1.43 3.92 3.20 3.70 0.00 ! 0.00 1 0.18 1 0.00 | 0.00 0.00 I 0.00 15.05 | 0.15 2.21 I 0.11 2.70 5.59 0.51 7.50 8.93 0.04 0.06 0.01 0.17 0.23 0.81 0.04 1 3.54 | 0.00 | 0.00 1.84 0.08 I 3.18 0.18 j 0.00 ! 0.00 0.18 7.20 0.82 0.18 3.46 4.35 2.69 I 4.88 0.00 0.00 4.03 ! 0.21 14.63 0.00 0.29 8.98 1.12 0.08 0.00 0.01 0.28 0.02 5.95 1 0.21 2.52 | 0.06 i 3.45 | 1.16 1 0.03 I 1476D I 6.79 1 4.27 0.21 | 3.96 | 24.75 I 0.69 i 2.95 1 15.59 I 0.33 i 1493 1497D 1512 1534 1556 4.24 | 4.49 0.13 1 1.33 | 42.11 | 0.40 3.72 6.10 2.18 2.80 1562D | 2.50 1584D 1594 Average 6.91 3.95 4.99 6.45 0.17 0.98 0.04 16.51 0.18 2.26 0.25! 1-15 1.43 | 0.03 | 1.30 • 16.43 | 0.29 2.17 4.82 9.09 0.11 0.13 0.25 1.30 3.67 1.74 1.88 0.00 | 0.00 5.76 25.33 10.77 33.85 2.46 5.75 13.32 0.09 0.21 0.10 0.31 0.06 0.07 0.14 1.05 0.18 1.36 1.24 1.70 1.60 4.06 1.53 1.61 36.19 | 0.27 0.00 8.12 9.68 1.18 18.75 2.71 1.97 4.54 0.00 | 0.08 i 0.08 0.01 0.21 0.08 0.02 0.07 In Case 2, mean concentrations are calculated using half the analytical detection limit (AOL) for tube concentrations below ADL.------- TABLE B-3. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE I1 Chicago, IL (C4DL) Sample Date 24-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 ll-May-90 23-May-90 04-Jun-90 16-Jun-90 28-Jun-90 22-Jul-90 03-Aug-90 l6-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-0ct-90 26-Oct-90 08-Nov-90 Week Day St Th T Sn F W M St Th Sn F Th M St Th T Sn F Th 19-Nov-90 | M Ol-Dec-90 13-Dec-91 28-Dec-90 04-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 St Th F F F W M St ID Number 1175 1196 1207 1219 1228 1244 1261 1268 Formaldehyde Mean* Cone (ppb) 3.84 4.05 3.89 2.87 3.38 3.05 2.45 7.50 Absolute3 Percent Diff 6.25 12.11 9.01 0.70 6.81 Stds Dev (ppb) 0.17 0.35 0.25 0.01 0.16 20.33 0.44 0.41 0.01 5.87 0.31 1285 5.79 | 5.53 0.23 1314 1324 1343 1352 1375 1391 1407 1421 1436 1452 1475 1483 7.60 13.64 3.29 0.18 16.28 1.57 5.18 | 4.83 7.43 5.25 4.92 5.09 4.59 4.34 4.01 3.88 15.88 4.95 19.11 0.18 Acetaidehyde Mean1 Cone (ppb) 2.59 1.82 1.68 1.43 1.76 1.50 0.93 \bsoiute3 Percent Diff 1.93 11.57 17.31 54.04 0.57 Std3 Dev (ppb) 0.04 0.15 0.21 0.54 0.01 2.01 0.02 3.24 0.02 Acetone Mean2 Cone (ppb) 2.92 2.99 2.00 2.03 2.03 4.98 3.56 3.40 i 8.24 0.20 3.49 2.47 | 6.90 0.12 3.00 4.83 2.34 0.05 33.54 1.15 1.85 | 10.30 0.83 | 2.16 0.18 0.66 6.88 | 0.25 8.71 3.46 1.50 13.68 0.28 0.11 0.04 0.37 3.86 31.61 0.86 1 1504 | 3.48 5.17 0.13 1525 1537D 1547 1557 1577 1593 Average 3.23 4.62 3.78 4,81 1.24 1.95 3.70 16.02 3.43 | 5.55 3.18 4.75 2.52 8.33 ! 0.03 0.06 0.10 0.54 0.13 0.06 0.30 2.25 2.27 1.86 2.33 2.31 1.94 2.07 1.89 11.11 2.67 11.04 4.85 7.73 0.00 4.12 15.98 0.13 0.17 0.04 0.18 0.06 0.13 0.00 0.06 0.23 3.53 3.85 3.37 3.76 3.13 2.03 7.82 6.96 2.96 3.53 3.94 2.47 52.52 0.70 1.98 1.40 44.29 1.58 2.08 1.40 2.03 1.32 1.00 2.04 0.63 0.96 2.15 0.44 i 1.00 0.01 0.01 0.02 1.23 1.24 1.32 1.48 0.02 i 1.77 0.76 3.02 11.26 0.01 0.02 0.17 0.94 0.83 2.91 Absolute3 Percent Diff 7.89 26.09 2.51 69.63 18.27 5.03 Std3 Dev (ppb) 0.16 0.55 0.04 1.00 0.26 0.18 2.25 i 0.06 23.50 0.58 1 10.50 24.71 64.09 13.58 8.00 9.38 14.07 4.60 0.34 12.20 0.00 0.26 0.67 1.53 0.36 0.18 0.13 0.78 0.23 0.01 0.30 0.00 15.01 | 0.26 1 12.12 0.17 3.02 0.02 8.13 0.00 19.70 2.83 6.38 2.41 13.79 0.07 0.00 j 0.18 | 0.04 0.04 0.01 0.29 1 In Case 1, mean concentrations are calculated using detected tube concentrations only. : "-" indicates concentration below analytical detection limit (ADL). 5 "*" indicates insufficient data to perform calculation.------- TABLE B-4. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 2' Chicago, IL (C4IL) Sample Date 24-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 ll-May-90 23-Mav-90 04-Jun-90 16-Jun-90 28-Jun-90 22-Jul-90 03-Aug-90 16-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 08-Nov-90 l9-Nov-90 Ol-Dec-90 13-Dec-91 28-Dec-90 04-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Fefa-91 Week Day St Th T Sn F W M St Th Sn F Th M St Th T Sn F Th | M St Th | F F F 1 w M St ID Number 1175 1196 1207 1219 1228 1244 1261 1268 1285 1314 1324 1343 1352 1375 1391 1407 1421 1436 1452 1475 i 1483 1 1504 1525 1537D 1547 1557 1577 | 1593 Average Fo Mean Cone (ppb) 3.84 4.05 3.89 2.87 3.38 3.05 2.45 7.50 5.79 7.60 13.64 5.18 7.43 5.25 4.92 5.09 4.59 4.34 4.01 3.88 3.86 3.48 i 3.23 4.62 3.78 | 4.81 3.43 3.18 4.75 rmaideavc Absolute Percent Diff 6.25 12.11 9.01 0.70 6.81 20.33 0.41 5.87 | 5.53 3.29 16.28 4.83 15.88 4.95 19.11 6.88 8.71 3.46 1.50 13.68 31.61 1 5.17 1.24 1.95 3.70 16.02 5.55 2.52 8.33 e Std Dev (ppb) 0.17 0.35 0.25 0.01 0.16 0.44 0.01 ! 0.31 j 0.23 | 0.18 1.57 0.18 0.83 0.18 0.66 0.25 0.28 0.11 0.04 0.37 0.86 0.13 0.03 0.06 0.10 0.54 0.13 0.06 0.30 A< Mean Cone (ppb) 2.59 1.82 1.68 1.43 1.76 1.50 0.93 3.40 2.47 3.00 4.83 1.85 2.16 2.25 2.27 1.86 2.33 2.31 1.94 2.07 1.89 I 1.40 1.58 2.08 1.40 2.03 1.32 1.00 2.04 ;etaidehvd Absolute Percent Diff 1.93 11.57 17.31 54.04 0.57 2.01 3.24 8.24 6.90 2.34 33.54 10.30 11.11 2.67 11.04 4.85 7.73 0.00 4.12 15.98 52.52 44.29 0.63 0.96 2.15 1.48 0.76 3.02 11.26 e I Std Dev (ppb) 0.04 I 0.15 0.21 0.54 0.01 0.02 0.02 0.20 0.12 0.05 1.15 0.13 0.17 0.04 0.18 0.06 0.13 0.00 0.06 0.23 0.70 0.44 0.01 I 0.01 0.02 0.02 0.01 0.02 0.17 Mean Cone (ppb) 2.92 2.99 2.00 2.03 2.03 4.98 1 3.56 3.49 3.53 3.85J 3.37 3.76 3.13 2.03 7.82 | 6.96 1 2.96 3.53 3.94 2.47 1.98 1 1.00 | 1.23 ! 1.24 | 1.32 1 1.77 | 0.94 1 0.83 2.91 Acetone Absolute Percent Diff 7.89 26.09 2.51 | 69.63 | 18.27 5.03 2.25 23.50 10.50 24.71 64.09 13.58 8.00 9.38 14.07 4.60 0.34 12.20 0.00 15.01 12.12 3.02 8.13 0.00 19.70 2.83 6.38 2.41 13.79 1 Std Dev 1 (ppb) 0.16 I 0.55 0.04 1.00 0.26 0.18 0.06 0.58 1 0.26 0.67 | 1.53 0.36 0.18 0.13 0.78 0.23 0.01 0.30J 0.00 0.26 0.17 1 0.02 0.07 1 | 0.00 0.18 0.04 1 0.04 1 0.01 0.29 ' In Case 2. mean concentrations arc calculated using half the analytical detection limit (ADL) for tube concentrations below ADL.------- TABLE B-5. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE I1 Camden, NJ (CANJ) Sample Date 12-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 Week Day M St Th T Sn ll-May-9o| F 23-May-90 04-Jun-90 16-Jun-90 28-Jun-90 10-Jul-90 22-Jul-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 W M ID Number 1166 1178 1190D 1200 1215 1232 1242 1260 Formaldehyde Mean2 Cone (ppb) 8.56 3.41 4.34 4.94 3.74 2.36 3.08 Absolute3 Percent Diff 9.35 24.63 0.00 3.85 5.35 10.17 0.65 Std3 Dev (ppb) 0.57 0.59 0.00 0.13 0.14 0.17 0.01 2.86 2.80 0.06 St | 1270 5.29 Th | 1282 T Sn F W M St Th T Sn F W l9-Nov-90 M Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 St Th T Sn F W M St 1288 1310 1319 1337 1361 1369 1384 1403 1422 9.48 8.85 9.12 9.81 8.30 7.07 3.16 3.24 4.03 5.05 1.13 0.04 0.84 0.57 3.18 15.49 2.05 4.53 4.75 6.79 0.00 0.20 1438 | 2.35 | 2.55 1463D 1472 Acetaldehyde Acetone Mean2 Cone (ppb) 4.59 1.87 1.98 2.53 1.75 0.93 1.27 1.24 1.94 0.06 3.87 0.04 3.86 0.21 1.07 0.12 0.23 0.11 0.16 0.00 0.01 0.04 3.63 I 0.83 0.02 3.36 3.96 4.17 3.18 1.14 2.27 1.89 2.91 1.44 2.11 3.15 1.90 I 0.04 1.81 1494 4.82 0.21 1505 5.08 1513D | 3.30 1531 1548 1570D 1586D 1597 Average 4.36 2.52 5.25 2.82 2.99 4.90 4.93 5.16 0.01 0.18 0.12 3.44 0.11 9.52 | 0.17 5.91 0.36 6.37 4.58 0.22 0.01 0.13 0.16 2.60 2.80 1.87 2.26 Absolute3 Percent Diff 8.71 0.54 5.05 6.73 Std3 Dev (ppb) Mean2 Cone (ppb) 0.28 | 4.19 0.01 0.07 0.12 18.91 | 0.23 17.20 I 0.11 5.53 1 0.05 9.68 1 0.08 2.36 2.24 2.38 1.49 1.40 2.01 1.13 8.79 ! 0.12 1.63 1.55 | 0.04 | 3.97 17.38 I 0.47 8.93 7.33 6.48 2.83 9.69 14.57 1.06 0.34 0.21 0.21 0.19 0.06 0.08 0.23 0.01 2.96 Absolute3 Percent Diff 10.75 22.88 11.61 0.42 10.10 17.14 23.88 11.56 6.13 11.08 3.72 2.56 I 5.47 5.31 4.44 2.98 2.01 3.21 2.41 0.01 | 1.40 2.78 j 0.03 | 1.79 2.84 0.04 1 2.04 6.63 0.08 1 1.19 5.01 0.09 1.79 4.83 3.10 1.36 5.88 2.45 | 2.86 1.36 1.48 2.34 2.94 8.11 6.60 0.04 0.06 1.78 1.90 1.27 0.05 1 1.75 0.06 0.05 0.03 0.08 0.11 1.27 2.40 1.05 1.33 2.26 40.53 2.03 13.11 6.97 19.31 0.42 2.86 0.00 7.37 5.04 7.32 7.37 10.28 2.29 4.72 0.42 0.96 6.02 9.06 Std3 Dev (ppb) 0.32 0.38 0.18 0.01 0.11 0.17 0.34 0.09 0.07 0.31 0.08 0.10 | 1.52 0.06 0.28 0.10 0.44 0.01 0.03 0.00 0.11 I 0.04 0.09 0.10 0.09 0.03 0.04 0.01 0.01 0.06 0.17 In Case 1, mean concentrations are calculated using detected tube concentrations only. "-" indicates concentration below analytical detection limit (ADL). "*" indicates insufficient data to perform calculation.------- TABLE B-6. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 21 Camden, NJ (CANJ) Sample Dale 12-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 ll-May-90 23-May-90 04-Jun-90 16-Jun-90 28-Jun-90 10-Jul-90 22-Jui-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 19-Nov-90 Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 Week Day M St Th T Sn F W M St Th T Sn F W M St Th T So F W M St Th T So F W M St ID Number 1166 1178 1190D 1200 1215 1232 1242 1260 1270 1282 1288 1310 1319 1337 1361 1369 1384 1403 1422 1438 1463D 1472 1494 1505 1513D 1531 1548 1570D 1586D 1597 Average Formaldehyde Mean Cone fa*) 8.56 3.41 4.34 4.94 3.74 2.36 3.08 2.86 Absolute Percent Diff 9.35 24.63 0.00 3.85 5.35 10.17 0.65 Std Dev (ppb) 0.57 0.59 0.00 0.13 0.14 0.17 0.01 2.80 | 0.06 5.29 1 1.13 Acetaldebyde Mean Cone (ppb) 4.59 1.87 1.98 2.53 1.75 0.93 1.27 1.24 0.04 1.94 9.48 J 0.84 | 0.06 8.85 | 0.57 9.12J 3.18 9.81 8.30 7.07 3.16 3.24 4.03 5.05 2.35 3.63 3.15 4.82 5.08 3.30 4.36 2.52 5.25 2.82 2.99 4.90 15.49 2.05 4.53 4.75 6.79 0.00 0.20 2.55 0.83 0.04 0.21 1.07 0.12 0.23 0.11 0.16 0.00 0.01 0.04 3.87 3.86 3.36 3.96 4.17 3.18 1.14 2.27 1.89 2.91 1.44 0.02 2.11 1.90 0.04 1.81 0.21 4.93 5.16 3.44 9.52 5.91 0.36 6.37 4.58 0.01 2.60 0.18 0.12 0.11 0.17 0.22 0.01 0.13 0.16 Absolute Percent Diff 8.71 0.54 5.05 6.73 18.91 17.20 5.53 9.68 8.79 1.55 17.38 8.93 7.33 6.48 2.83 9.69 14.57 1.06 0.34 2.78 2.84 6.63 5.01 2.80 1.79 1.87 2.26 1.36 2.45 1.36 1.48 2.34 4.83 3.10 5.88 2.86 2.94 8.11 6.60 Std Dev (ppb) 0.28 0.01 0.07 0.12 0.23 0.11 Acetone Mam Cane (ppb) 4.19 2.36 2.24 2.38 1.49 1.40 0.05 | 2.01 0.08 0.12 0.04 0.47 0.21 0.21 0.19 0.06 0.08 0.23 0.01 0.01 0.03 0.04 0.08 0.09 0.04 0.06 0.05 0.06 0.05 0.03 0.08 0.11 1.13 1.63 3.97 2.96 2.56 5.31 4.44 2.98 2.01 3.21 2.41 1.40 1.79 2.04 1.19 1.78 1.90 1.27 1.75 1.27 2.40 1.05 1.33 2.26 Absolute Percent Diff 10.75 22.88 11.61 0.42 10.10 17.14 23.88 11.56 6.13 11.08 3.72 5.47 40.53 2.03 13.11 6.97 19.31 0.42 2.86 0.00 7.37 5.04 7.32 7.37 10.28 2.29 4.72 0.42 0.96 6.02 9.06 Std Dev (ppb) 0.32 0.38 0.18 0.01 0.11 0.17 0.34 0.09 0.07 | 0.31 0.08 0.10 1.52 0.06 0.28 0.10 0.44 0.01 0.03 0.00 1 0.11 1 0.04 | 0.09 | 0.10 0.09 0.03 0.04 0.01 0.01 0.06 0.17 In Case 2, mean concentration* are calculated using half the analytical detection limit (ADL) for tube concentrations below ADL.------- TABLE B-7. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE I1 Houston, TX (H1TX) Sample Dale 12-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 ll-May-90 23-May-90 04-Jun-90 16-Jun-90 22-Jul-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 19-Nov-90 Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 Week Day M St Th ID Number 1170D 1184 1187 T | 1210 F W M St 1230D 1245 1255 Formaldehyde Mean2 Cone (ppb) 0.65 1.41 1.12 1.80 0.63 Absolute3 Percent Diff Std3 Dev (ppb) 89.23 1 0.41 34.04 7.14 12.22 0.34 0.06 Acetaldehyde Mean3 Cone (ppb) 0.43 0.64 - 0.16) 0.65 4.80 | 0.02 2.32 | 17.71 0.29 0.37 1.01 1.94 7.75 | 0.11 j 0.79 1267 | 1.62 0.62 Sn | 1308 F W M St Th T Sn F W M St 1323 1334 1357 1373D 1390 1413 1426 1435 1451 1474 1488 1.08 1.15 1.91 1.42 1.03 1.25 1.45 1.55 2.01 1.31 1.14 1.65 0.01 | 0.46 11.11 0.08 I 0.38 2.62 4.72 15.49 1.94 6.40 18.69 6.45 1.99 3.83 0.02 0.06 0.16 0.01 0.06 0.19 0.07 0.03 0.04 12.28 | 0.10 0.61 | 0.01 Th 1502 2.08 1 19.23 I 0.28 T Sn F W M St 1519 1539D 1544 1558 1574 1598 Average 0.38 1.21 0.80 - 0.68 1.01 1.29 1.21 0.80 0.93 0.68 0.57 1.33 2.26 I 0.02 I 0.87 1.52 I 5.26 I 0.06 1.52 0.56 2.55 1.39 1.46 4.62 12.61 0.05 0.05 5.11 1 0.09 1.44 I 0.01 11.49 0.10 0.44 0.42 0.38 1.15 0.70 0.73 Absolute3 Percent Diff 11.76 61.42 * 61.54 100.00 34.83 25.32 41.76 0.00 100.00 11.57 1.26 * 0.00 12.94 11.67 29.75 7.50 8.60 2.94 17.54 1.16 4.55 7.23 10.53 2.62 0.00 22.66 Std3 Dev (ppb) 0.04 0.28 * 0.28 0.00 0.25 0.14 0.13 Acetone Mean2 Cone (ppb) 0.62 0.88 0.86 0.74 0.80 1.16 0.58 Absolute3 Percent Diff 100.00 37.71 48.84 31.29 2.50 37.23 15.65 Std» Dev (ppb) 0.00 0.23 0.30 0.16 0.01 0.30 0.06 I 0.45 | 29.21 1 0.09 0.00 | 0.43 0.00 0.10 0.01 * 0.00 0.09 0.11 0.25 0.04 0.06 0.01 0.07 - 0.64 0.66 - - 1.24 0.82 0.59 0.74 0.42 - 100.00 | 0.00 | * 1.57 33.33 * * 19.35 6.13 44.07 10.81 16.87 * * 1 0.01 1 0.16 * * 0.17 0.04 0.18 0.06 0.05 * 0.38 | 100.00 | 0.00 0.01 I - 0.01 | - 0.02 0.03 0.02 0.00 0.08 - 0.39 0.83 0.43 0.68 * * * * 100.00 35.15 4.65 38.72 + * 1 0.00 1 0.21 0.01 0.10 ' In Case 1, mean concentrations are calculated using detected tube concentrations only. 2 "-" indicates concentration below analytical detection limit (AOL). '- "*" indicates insufficient data to perform calculation.------- TABLE B-8. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 21 Houston, TX (H1TX) Sample Date 12-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 ll-May-90 23-May-90 04-Jun-90 16-Jun-90 22-Jui-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-0ct-90 14-Oct-90 26-Oct-90 07-Nov-90 19-Nov-90 Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 Week Day M St Th T F W M St Sn F W M St Th T Sn F W M St Th T 1 Sn F W M 1 St ID Number 1170D 1184 1187 1210 1230D 1245 1255 1267 1308 1323 1334 1357 1373D 1390 1413 1426 1435 1451 1474 1488 1502 1519 1539D 1544 1558 1574 1598 Average Fo Mean Cone (ppb) 0.65 1.41 1.12 1.80 0.63 | 2.32 1.94 1.62 1.08 1.15 1.91 1.42 1.03 1.25 1.45 1.55 2.01 1.31 1.14 1.65 2.08 1.33 I 1.52 1.52 0.56 | 2.55 1.39 1.46 nnaidehyc Absolute Percent Diff 89.23 | 34.04 7.14 12.22 4.80 17.71 7.751 0.62 | 11.11 2.62 4.72 15.49 1.94 6.40 18.69 6.45 1.99 3.83 12.28 0.61 19.23 1 2.26 | 5.26 4.62 12.61 5.11 1.44 11.49 e Std Dev (ppb) 0.41 0.34 0.06 0.16 0.02 0.29 0.11 | 0.01 0.08 0.02 0.06 0.16 0.01 0.06 0.19 0.07 0.03 0.04 0.10 | 0.01 | 0.28 0.02 0.06 0.05 0.05 0.09 0.01 0.10 A( Mean Cone (ppb) 0.43 0.64 0.18 0.65 0.28 1.01 0.79 0.46 0.38 0.28 1.21 0.80 0.18 0.68 1.01 1.29 1.21 0.80 0.93 0.68 0.57 0.87 | 0.44 0.42 0.38 1.15 0.70 0.68 xtaldehyd Absolute Percent Diff 11.76 61.42 0.00 | 61.54 | 69.09 34.83 25.32 ! 41.76 I 0.00 I 71.43 I 11.57 I 1.26 0.00 0.00 12.94 11.67 29.75 7.50 8.60 2.94 17.54 1 1.16 4.55 7.23 10.53 2.62 0.00 18.78 e 1 Std Dev (ppb) 0.04 | 0.28 0.00 0.28 0.13 0.25 0.14 0.13 0.00 0.14 0.10 0.01 0.00 0.00 0.09 0.11 0.25 0.04 0.06 0.01 0.07 0.01 0.01 | 0.02 | 0.03 | 0.02 0.00 0.08 Mean Cone (ppb) 0.40 0.88 0.86 | 0.74 0.80 1.16 0.58 0.45 0.31 0.18 0.64 0.66 0.18 0.18 1.24 0.82 0.59 0.74 0.42 0.18 0.28 0.18 0.18 0.18 0.29 0.83 0.43 0.53 Acetone Absolute Percent Diff 110.00 37.71 48.84 31.29 2.50 37.23 15.65 29.21 81.97 0.00 1.57 33.33 0.00 0.00 19.35 6.13 44.07 10.81 16.87 0.00 71.43 0.00 | 0.00 0.00 73.68 35.15 4.65 26.35 | Std Dev (ppb) 0.31 0.23 0.30 0.16 0.01 0.30 0.06 0.09 0.18 I 0.00 1 0.01 | 0.16 0.00 0.00 0.17 0.04 0.18 0.06 0.05 0.00 | _0.14 ! I 0.00 1 ! o.oo I | 0.00 0.15 0.21 0.01 0.10 In Case 2. mean concentrations are calculated using half the analytical detection limit (ADL) for tube concentrations below ADL.------- TABLE B-9. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 1' Orlando, FL (ORFL) Sample Date 10-Jul-90 16-M-90 22-Jul-90 28-Jul-90 03-Aug-90 Week Day T M Sn St F 09-Aug-90 | Th l5-Aug-90 W 27-Aug-90 1 M ID Number 1290 1302 1307 1316 1320 1332 1350 Formaldehyde Mean1 Cone (PI*) 3.55 2.52 3.54 2.82 3.15 3.52 Absolute3 Percent Diff 7.89 13.12 2.55 46.10 8.25 Stds Dev (ppb) 0.20 0.23 0.06 0.92 0.18 8.25 | 0.21 3.34 I 0.90 | 0.02 1359 I 4.48 1 4.25 02-Sep-90 1 Sn 1363 08-Sep-90 I St | 1377 14-Sep-90 F 20-Sep-90 | Th 26-Sep-90 08-Oct-90 14-Oct-90 20-Oct-90 26-Oct-90 Ol-Nov-90 07-Nov-90 13-Nov-90 Ol-Dec-90 W M Sn St F Th W T St i 13-Dec-90 1 Th 25-Dec-90 T 06-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 | Sn F W M St 1383 1386 1397 1418 1424 1432 1446 1449D 1465 1466 1484 1508D 1522 1533 1554D 1567 1580 1596 Average 0.13 2.78 4.32 i 0.08 4.54 3.99 0.42 3.44 1.85 33.54 2.02 3.21 2.35 3.37 4.34 2.12 0.44 | 0.01 3.26 * 4.37 2.16 3.40 8.44 0.94 0.43 5.05 0.09 * 0.11 0.03 0.81 0.12 0.02 0.01 0.12 3.46 0.11 Acetaldehyde Mean1 Cone (Ppb) - 0.55 1.09 0.73 1.00 1.45 1.00 1.20 0.91 0.95 1.14 0.53 1.00 0.49 9.41 0.93 1.49 0.96 1.24 1.77 1.89 0.03 | 1.02 7.01 0.43 0.02 2.91 6.38 1.81 3.48 3.59 3.60 2.44 4.40 2.67 2.21 1.44 I 7.24 3.06 0.12 0.03 0.04 0.18 0.08 6.56 | 0.11 5.67 0.15 2.67 0.67 1.35 1.26 1.47 1.04 1.49 Absolute3 Percent Diff * 16.51 12.84 70.34 1.01 4.14 4.00 Std3 Dev (ppb) * 0.06 0.10 0.36 0.01 0.04 0.03 Acetone Mean1 Cone (ppb) 0.37 0.69 0.57 - - 0.77 - Absolute3 Percent Diff + * * * * Stds Dev (ppb) * * * * * 31.17 | 0.17 I * * 10.88 | 0.09 | 0.47 ] 8.51 1 0.03 1 23.20 | 0.15 1 0.43 | * * 25.26 0.17 7.02 * 4.00 2.06 101.97 9.73 35.69 1.05 4.84 2.83 1.96 3.79 0.75 8.96 0.74 6.35 2.05 7.69 14.22 0.06 * 0.03 0.01 6.78 0.06 0.37 0.01 0.04 0.04 0.01 0.08 0.01 0.04 0.01 0.06 0.02 0.06 0.33 0.67 I 13.53 | 0.06 | 0.77 11.76 1.08 | * 1.04 0.44 10.79 0.60 2.04 1.13 1.03 1.44 0.06 * 4.83 i 0.04 * * 8.40 6.39 12.39 * * 0.04 0.09 0.10 . 15.53 1 0.11 27.18 1 0.28 0.49 | 28.57 | 0.10 1.23 | 93.88 | 0.81 0.44 i 22.73 | 0.07 0.43 1.94 0.61 1.97 1.13 1.30 13.95 ! 0.04 1 21.65 | 0.30 31.40 12.72 0.13 0.18 14.16 I 0.11 21.04 0.15 1 In Case 1. mean concentrations are calculated using detected tube concentrations only. : "-" indicates concentration below analytical detection limit (ADL). ' "*" indicates insufficient data to perform calculation.------- TABLE B-10. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 2' Orlando, FL (ORFL) Sample Date 10-Jul-90 16-M-90 22-Jul-90 28-Jul-90 03-Aug-90 09-Aug-90 15-Aug-90 27-Aug-90 02-Sep-90 08-Sep-90 14-Sep-90 20-Sep-90 26-Sep-90 08-Oct-90 14-0ct-90 20-Oct-90 26-Oct-90 Ol-Nov-90 07-Nov-90 13-Nov-90 Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 Week Day T M So St F Th W M Sn St F Th W M Sn St F Th W T St Th T Sn F W M St n> Number 1290 1302 1307 1316 1320 1332 1350 1359 1363 1377 1383 1386 1397 1418 1424 1432 1446 1449D 1465 1466 1484 Formaldehyde Mean Cone (ppb) 3.55 2.52 3.54 2.82 3.15 3.52 3.34 4.48 2.78 4.54 3.99 0.30 3.44 1.85 33.54 2.02 3.21 2.35 3.37 4.34 2.12 1508D 7.01 1522 1533 1554D 1567 1580 1596 Average ]_ 6.38 1.81 3.48 3.59 3.60 2.44 4.39 Absolute Percent Diff 7.89 13.12 2.55 46.10 8.25 8.25 0.90 4.25 4.32 0.44 3.26 80.00 4.37 2.16 3.40 8.44 0.94 0.43 5.05 3.46 1.89 0.43 2.67 2.21 1.44 7.24 3.06 6.56 8.32 Sid Dev (Ppb) 0.20 0.23 0.06 0.92 0.18 0.21 0.02 0.13 0.08 0.01 0.09 0.17 0.11 0.03 0.81 0.12 0.02 0.01 0.12 0.11 0.03 0.02 0.12 0.03 0.04 0.18 0.08 0.11 0.15 Ace** ''i'hyde Mean Cone (ppb) 0.18 0.55 1.09 0.73 1.00 1.45 1.00 1.20 0.91 0.95 1.14 0.36 1.00 0.49 9.41 0.93 1.49 0.96 1.24 1.77 1.02 2.91 2.67 0.67 1.35 1.26 1.47 1.04 1.43 Absolute Percent Diff 0.00 16.51 12.84 70.34 1.01 4.14 4.00 10.88 Std Dev (ppb) 0.00 0.06 0.10 0.36 Acetone Mean Conic (ppb) 0.28 0.44 0.38 0.18 0.01 ) 0.18 0.04 0.03 0.09 0.77 0.18 0.47 23.20 0.15 1 0.31 25.26 7.02 98.59 4.00 2.06 101.97 9.73 35.69 1.05 4.84 2.83 1.96 3.79 0.75 3.96 0.74 6.35 2.05 7.69 16.72 Absolute Percent Diff 69.09 117.24 104.00 0.00 0.00 31.17 0.00 8.51 81.97 0.17 0.67 j 13.53 0.06 I 0.77 0.25 0.63 0.03 0.01 6.78 0.06 0.37 0.01 .0.04 1.04 0.31 5.49 0.60 2.04 1.13 1.03 0.04 | 1.44 0.01 0.08 0.01 0.04 0.01 0.06 0.02 0.06 0.32 0.49 1.23 0.44 0.43 1.94 0.61 1.97 1.13 0.95 11.76 142.86 4.83 83.87 193.44 8.40 6.39 12.39 15.53 27.18 28.57 93.88 22.73 13.95 21.65 31.40 12.72 14.16 41.83 Std Dev (Ppb) 0.13 0.36 0.28 0.00 0.00 0.17 0.00 0.03 0.18 0.06 0.06 0.64 0.04 0.18 7.50 0.04 0.09 0.10 0.11 0.28 0.10 0.81 0.07 0.04 0.30 0.13 0.18 0.11 0.43 1 In Case 2, mean concentration* are calculated using naif the analytical detection limit (ADL) for tube concentration! below ADL.------- TABLE B-ll. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE I1 PensacoU, FL (PEFL) Sample- Date 10-Feb-90 22-Feb-90 12-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 ll-May-90 23-Mav-90 04-Jun-90 16-Jun-90 28-Jun-90 10-Jul-90 16-Jui-90 22-Jul-90 28-Jul-90 03-Aug-90 09-Aug-90 15-Aug-90 21-Aug-90 27-Aug-90 02-Sep-90 08-Sep-90 14-Sep-90 20-Sep-90 26-Sep-90 02-Oct-90 08-Oct-90 14-Oct-90 20-Oct-90 26-Oct-90 Ol-Nov-90 07-Nov-90 14-Nov-90 Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 12-Feb-91 23-Feb-91 Week Day St Th M St Th T Sn F W M St Th T M Sn St F Th W T M Sn St F Th W T M Sn St F Th W W St Th T Sn F W T St ID Number 1158 1159 1174 1186D 1194 1206 1213 1225 1250 1257 1263 1279 1298 1301 1313 1318 1327 1330 1339 1349 1353 1364 1368 1381 1388 1402 Formaldehyde Mean* Cone (ppb) 0.91 1.38 2.52 1.69 3.86 3.01 2.05 2.18 2.86 1.87 5.16 0.91 3.46 1.98 1.57 5.03 3.61 4.15 4.35 2.63 1.71 2.58 3.60 1.81 2.62 3.73 1406 1.67 1415 1.71 1423 1431 1444 1448 1458 1467 1495 1500 1517 1527 1545D 1564 1582 1601D Average 15.15 2.37 1.67 2.26 2.11 2.22 1.57 1.49 0.93 1.10 1.23 0.74 2.96 0.88 2.65 Absolute3 Percent Diff 43.96 5.80 3.58 12.46 3.11 3.32 8.31 18.85 5.59 20.91 2.91 16.57 2.89 7.07 13.42 18.11 2.77 0.96 1.61 2.67 7.62 5.83 9.18 13.85 7.27 2.42 1.20 5.85 * 0.84 5.99 3.99 6.18 7.21 0.64 6.71 11.89 0.91 2.45 39.46 5.75 0.00 8.30 Std* Dev (ppb) 0.28 0.06 0.06 0.15 0.08 0.07 0.12 0.29 0.11 0.28 0.11 0.11 0.07 0.10 0.15 0.64 0.07 0.03 0.05 0.05 0.09 0.11 0.23 0.18 0.13 0.06 0.01 0.07 * 0.01 0.07 0.06 0.09 0.11 0.01 0.07 0.08 0.01 0.02 0.21 0.12 0.00 0.11 Acetaldehyde j Mean2 Cone (ppb) 0.60 - 1.06 1.57 1.52 1.15 0.75 0.58 0.77 0.58 1.12 0.76 0.41 0.48 - 1.27 0.50 1.08 1.18 0.74 0.46 0.43 0.89 0.38 0.73 1.46 0.49 0.51 2.73 0.76 0.59 1.14 0.92 1.29 0.88 0.85 0.67 0.49 0.73 0.39 1.81 0.69 0.88 Vbfiotute* Percent Diff 23.33 * 18.01 19.81 4.62 7.86 36.24 19.13 2.60 0.00 17.04 * 9.76 14.74 * 48.82 18.18 12.09 16.17 20.41 24.18 * 8.99 * 4.14 2.74 8.16 9.90 * 6.62 18.80 3.51 6.52 8.56 9.09 2.35 7.52 6.19 6.90 0.00 2.77 1.46 11.87 Std' Dev (ppb) 0.10 * 0.13 0.22 0.05 0.06 0.19 0.08 0.01 0.00 Acetone Mean' Cone (ppb) 1.13 1.75 1.75 1.89 3.00 1.51 0.66 1.09 1.37 0.40 0.13 I 1.18 * 0.63 0.03 0.05 * 0.44 0.06 0.09 0.13 0.11 0.08 * 0.06 * 0.02 0.03 1.03 - 2.79 - 2.52 1.55 0.41 0.43 0.55 0.81 - 1.46 3.39 Absolute-1 Percent Diff 16.89 7.45 70.49 0.00 4.67 2.65 12.12 23.04 8.76 12.66 64.41 * * 15.53 * 13.29 * 13.92 27.10 * 7.06 31.19 21.12 * 25.43 3.54 0.03 - * 0.04 0.49 * 0.04 0.08 0.03 0.04 0.08 0.06 0.01 0.04 0.02 0.04 0.00 0.04 0.01 0.07 10.56 2.31 1.46 2.64 1.85 1.88 0.46 2.55 0.88 0.49 1.34 - 2.00 1.31 1.71 8.16 * 0.43 2.74 5.30 5.41 5.87 4.35 3.14 12.57 8..16 0.75 5.00 0.77 13.45 Std3 Dev (ppb) 0.13 0.09 0.87 0.00 0.10 0.03 0.06 0.18 0.08 0.04 0.54 * i * 0.11 * 0.26 * 0.25 0.30 * 0.02 0.12 0.12 * 0.26 0.08 * 0.03 * 0.01 0.03 0.10 0.07 0.08 0.01 0.06 0.08 0.03 0.01 0.07 0.01 0.13 1 In Case i, mean concentration* are calculated using detected tube concentrations only. 2 *-" indicate* concentration below analytical detection limit (ADD. ' "*" indicate* insufficient data to perform calculation.------- TABLE B-12. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 2' Pensacola, FL (PEFL) Sample Date 10-Feb-90 22-Feb-90 12-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 ll-Mav-90 23-Mav-90 04-Jun-90 16-Jun-90 i 28-Jun-90 10-Jul-90 16-JuI-90 22-Jul-90 28-Jul-90 03-Aug-90 09-Aug-90 15-Aug-90 21-Aug-90 27-Aug-90 02-Sep-90 08-Sep-90 14-Sep-90 20-Sep-90 26-Sep-90 02-Oct-90 08-Oct-90 14-Oct-90 20-Oct-90 26-Oct-90 Ol-Nov-90 07-Nov-90 14-Nov-90 Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 12-Feb-9l 23-Feb-91 Week Day St Th M St Th T So F W M St Th T M Sn St F Th W T M Sn St F Th W T M Sn St F Th W W St Th T Sn F W T St ID lumber 1158 1159 1174 1186D 1194 1206 1213 1225 1250 1257 1263 1279 1298 1301 1313 1318 1327 1330 1339 1349 1353 1364 1368 1381 1388 1402 1406 1415 1423 1431 1444 1448 1458 1467 1495 1500 1517 1527 1545D 1564 1582 1601D Average Formaldehyde Mean Cone (ppb) 0.91 1.38 2.52 1.69 3.86 3.01 2.05 2.18 2.86 1.87 5.16 0.91 3.46 1.98 1.57 5.03 3.61 4.15 4.35 2.63 1.71 2.58 3.60 1.81 2.62 3.73 1.67 1.71 7.67 2.37 1.67 2.26 2.11 2.22 1.57 1.49 0.93 1.10 1.23 0.74 2.96 0.88 2.47 Absolute Percent DifF 43.96 5.80 3.58 12.46 3.11 3.32 8.31 18.85 5.59 20.91 2.91 16.57 Std Dev (P!*) 0.28 0.06 0.06 0.15 0.08 0.07 0.12 0.29 0.11 0.28 0.11 0.11 2.89 0.07 7.07 13.42 18.11 2.77 0.96 1.61 2.67 7.62 5.83 9.18 13.85 7.27 2.42 1.20 5.85 195.30 0.84 5.99 3.99 6.18 7.21 0.64 6.71 11.89 0.91 2.45 39.46 5.75 0.00 12.75 0.10 0.15 0.64 0.07 0.03 0.05 0.05 0.09 0.11 0.23 0.18 0.13 0.06 0.01 0.07 10.59 0.01 0.07 0.06 0.09 0.11 0.01 0.07 0.08 0.01 0.02 0.21 0.12 0.00 0.36 Acetaidehyde Acetone Mean Cone (Ppb) 0.60 0.18 1.06 1.57 1.52 1.15 0.75 0.58 0.77 0.58 1.12 0.47 0.41 0.48 0.18 1.27 0.50 1.08 1.18 0.74 0.46 0.31 0.89 0.28 0.73 1.46 0.49 0.51 1.46 0.76 0.59 1.14 0.92 1.29 0.88 0.85 0.67 0.49 0.73 0.39 1.81 0.69 0.81 Absolute Percent Diff 23.33 0.00 18.01 19.81 4.62 7.86 36.24 19.13 2.60 0.00 17.04 123.40 9.76 14.74 0.00 48.82 18.18 12.09 16.17 20.41 24.18 81.97 8.99 71.43 4.14 2.74 S.16 9.90 175.26 6.62 18.80 3.51 6.52 8.56 9.09 2.35 7.52 6.19 6.90 0.00 2.77 1.46 20.93 Std Dev (ppb) 0.10 0.00 0.13 0.22 0.05 0.06 0.19 0.08 0.01 0.00 0.13 Mean Cone (ppb) 1.13 1.75 1.75 1.89 3.00 1.51 0.66i 1.09 1.37 0.40' 1.18 0.41 0.41 0.03 0.18 0.05 0.00 0.44 0.06 0.09 0.13 0.11 0.08 0.18 0.06 0.14 0.02 0.03 1.03 0.18 2.79 0.18 2.52 1.55 0.30 0.43 0.55 0.81 0.18 1.46 3.39 0.03 0.18 0.04 1.80 0.04 0.08 0.03 0.04 0.08 0.06 0.01 0.04 0.02 0.04 0.00 0.04 0.01 0.12 0.49 5.37 2.31 1.46 2.64 1.85 1.88 0.46 2.55 0.88 0.49 1.34 0.18 2.00 1.31 1.36 Absolute Percent Diff 16.89 7.45 70.49 0.00 4.67 2.65 12.12 23.04 8.76 12.66 Std Dev (ppb) 0.13 0.09 •0.87 0.00 0.10 0.03 0.06 0.18 0.08 0.04 64.41 0.54 111.11 1 0.32 0.00 0.00 15.53 0.11 0.00 13.29 0.00 13.92 27.10 77.97 7.06 31.19 21.12 0.00 25.43 3.54 0.00 3.16 193.30 0.43 2.74 0.00 0.26 0.00 0.25 0.30 0.16 0.02 0.12 0.12 0.00 0.26 0.08 0.00 0.03 7.34 0.01 0.03 5.30 0.10 5.41 5.87 4.35 3.14 12.57 8.16 0.75 0.00 5.00 0.77 19.67 0.07 0.08 0.01 0.06 0.08 0.03 0.01 0.00 0.07 0.01 0.29 In Case 2, mean concentration* are calculated using half the analytical detection 1'""* (ADL) for tube concentration* below ADL.------- TABLE B-13. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE I1 Port Neches (PNTX) Sample Date 12-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 ll-May-90 23-May-90 04-Jun-90 16-Jun-90 28-Jun-90 10-Jul-90 22-Jul-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 30-Nov-90 Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 Week Day M St Th T Sn F W M St Th T Sn F W M St Th T Sn F W F St Th T Sn F W M St ID Number 1180 1183D 1192 1201 1212D 1224 1240 1256 1271 1281 1289 1305 1328 1335 1351 1371 1392 1414 1420 1437 1454 1469 1482 1499 1521 1532 1543 1559 1576 1592 Average Formaldehyde Mean* Cone (Ppb) 4.44 6.37 3.48 6,81 4.09 - 7.49 3.23 Absolute3 Percent Diff 80.95 115.54 8.62 70.10 93.76 * 75.22 2.79 4.27 55.74 7.35 3.22 2.43 4.66 7.86 8.46 4.12 3.51 2.83 5.42 5.67 4.61 Std* Dev2.54 5.20 0.21 3.37 2.71 * 3.98 0.06 Ace**i'lKhyde Mean2 Cone (ppb) 4.23 4.35 1.84 2.99 0.84 - 1.93 1.40 1.68 2.12 49.69 2.58 0.93 19.38 76.82 56.74 8.04 10.68 15.12 0.71 14.76 0.53 22.56 5.20 12.51 5.32 3.36 4.72 4.00 7.23 2.44 7.28 4.64 4.98 9.40 46.43 0.85 9.76 2.49 18.48 3.99 9.05 30.75 0.02 0.33 2.53 3.15 0.48 0.31 0.37 0.01 0.57 0.02 0.74 0.46 0.35 1.10 0.03 0.28 0.13 0.32 0.21 0.30 1.17 5.22 1.99 0.61 1.71 3.34 3.88 1.97 2.52 1.14 3.26 2.16 2.03 3.88 3.74 1.17 2.12 2.48 1.77 0.79 3.56 1.50 2.43 Absolute* Percent Diff 21.75 20.69 31.06 6.37 38.10 * 9.87 5.71 13.21 21.07 6.55 19.67 22.22 14.37 14.43 10.69 1.99 0.00 11.66 1.85 17.73 17.81 7.76 9.44 0.47 0.81 4.52 2.53 9.28 10.67 12.15 Std* Dev (ppb) 0.65 0.64 0.40 0.13 0.23 * 0.13 0.06 0.20 0.78 0.09 0.08 0.27 0.34 0.40 0.15 0.04 0.00 0.27 0.03 0.25 0.49 0.21 0.08 0.01 0.01 0.06 0.01 0.23 0.11 0.22 Acetone Mean3 Cone (ppb) 1.27 2.26 1.58 1.45 - - 1.39 0.41 0.48 1.78 - - 0.41 1.49 1.77 0.49 0.59 0.59 1.05 1.93 1.51 0.44 0.49 - 0.83 0.45 0.88 0.94 2.86 1.52 1.15 Absolute3 Percent Diff 43.48 27.94 19.68 13.79 * * 10.07 19.51 48.42 1.69 * * * 4.03 15.30 4.08 1.71 3.39 16.27 7.79 * * * * 3.64 4.44 2.27 21.28 4.20 3.30 13.16 Std3 Dev (ppb) 0.39 0.45 0.22 0.14 * * 0.10 0.06 0.16 0.02 | * * * 0.04 0.19 0.01 0.01 0.01 0.12 0.11 * * * * 0.02 0.01 0.01 0.14 0.08 0.04 0.11 In Case 1, mean concentrations are calculated using detected tube concentrations only. "-" indicates concentration below analytical detection limit (ADL). "*" indicates insufficient data to perform calculation. ------- TABLE B-14. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 21 Port Necfaes (PNTX) Sample Date 12-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 ll-May-90 23-Mav-90 04-Jun-90 16-Jun-90 28-Jun-90 10-Jul-90 22-Jui-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 30-Nov-90 Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 Week Day M St Th T Sn F W M St Th T Sn F W M St Th T Sn F W F St Th T Sn F W M St n> Shimber 1180 1183D 1192 1201 1212D 1224 1240 1256 1271 1281 1289 1305 1328 1335 1351 1371 1392 1414 1420 1437 1454 1469 1482 1499 1521 1532 1543 1559 1576 1592 Average Formaldehyde Mean Cone (ppb) 4.44 6.37 3.48 6.81 4.09 0.18 7.49 3.23 4.27 7.35 3.22 2.43 4.66 7.86 8.46 4.12 3.51 2.83 5.42 5.67 4.61 Absolute Percent Diff 80.95 115.54 8.62 70.10 93.76 0.00 75.22 2.79 55.74 49.69 0.93 19.38 76.82 56.74 8.04 10.68 15.12 0.71 14.76 0.53 22.56 5.20 12.51 5.32 3.36 4.72 4.00 7.23 2.44 7.28 4.64 4.82 9.40 46.43 0.85 9.76 2.49 18.48 3.99 9.05 29.72 Std Dev (Ppb) 2.54 5.20 0.21 3.37 2.71 0.00 3.98 0.06 1.68 2.58 0.02 0.33 2.53 3.15 0.48 0.31 0.37 0.01 0.57 0.02 0.74 Acei»idehyde Mean Cone (ppb) 4.23 4.35 1.84 2.99 0.84 0.18 1.93 1.40 2.12 5.22 1.99 0.61 1.71 3.34 3.88 1.97 2.52 1.14 3.26 2.16 2.03 0.46 1 3.88 0.35 1.10 0.03 0.28 0.13 0.32 0.21 0.30 1.14 3.74 1.17 2.12 2.48 1.77 0.79 3.56 1.50 2.36 Absolute Percent Diff 21.75 20.69 31.06 6.37 38.10 0.00 9.87 5.71 13.21 21.07 6.55 19.67 22.22 14.37 14.43 10.69 1.99 0.00 11.66 1.85 17.73 17.81 7.76 9.44 0.47 0.81 4.52 2.53 9.28 10.67 11.74 Std Dev (ppb) 0.65 0.64 0.40 0.13 0.23 0.00 0.13 0.06 Acetone Mean Cone (ppb) 1.27 2.26 1.58 1.45 0.18 0.18 1.39 0.41 Absolute Percent Diff 43.48 27.94 19.68 13.79 0.00 0.00 10.07 19.51 Std Dev (ppb) 0.39 0.45 0.22 0.14 0.00 0.00 0.10 0.06 0.20 0.48| 48.421 0.16 0.78 0.09 0.08 0.27 0.34 0.40 0.15 0.04 0.00 0.27 0.03 0.25 0.49 0.21 0.08 0.01 0.01 0.06 0.01 0.23 0.11 0.21 1.78 1.69 0.18 1 0.00 0.18 | 0.00 0.30 1.49 1.77 0.49 0.59 0.59 1.05 1.93 0.85 0.31 0.34 0.18 0.83 0.45 0.88 0.94 2.86 1.52 0.95 77.97 4.03 15.30 4.08 1.71 3.39 16.27 7.79 157.40 83.87 92.54 0.00 3.64 4.44 2.27 21.28 4.20 3.30 22.93 0.02 0.00 0.00 0.16 0.04 0.19 0.01 0.01 0.01 0.12 0.11 0.94 0.18 0.22 0.00 0.02 0.01 0.01 0.14 0.08 0.04 0.13 1 In Case 2, mean concentrations are calculated using half the analytical detection limit (ADL) for tube concentration* below ADL.------- TABLE B-15. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 1' Sauget, EL (SAIL) Sample Date 12-Mar-90 24-Mar-90 05-Apr-90 16-Apr-90 ll-Mav-90 23-May-90 04-Jun-90 16-Jun-90 28-Jun-90 10-Jui-90 24-Jul-90 03-Aug-90 14-Aug-90 27-Aug-90 08-Sep-90 25-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 19-Nov-90 Ol-Dec-90 13-Dec-90 27-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 12-Feb-91 23-Feb-91 Week Day M St Th M F W M St Th T T F T M St T T Sn F W M St Th Th 1 Sn F W T St ED Number 1165 1177 1195 1208 1226 1246 1262 1269 1280 1294 1315 1329 1344 1354 1372 1401 1404 1419 1441 1461D 1471 1491D 1501 1523 1535 1552D 1565 1581 1604D Average Fo Mean2 Cone (ppb) 1.16 1.52 2.16 1.39 0.97 1.97 3.05 3.09 1.88 7.23 2.48 1.97 2.81 6.15 3.16 3.45 4.54 2.84 2.08 1.88 3.18 | 1.13 1.48 1.83 1.71 1.88 1.76 1.72 1.94 2.51 nnaidehyd Absolute3 Percent Diff 12.07 13.16 22.22 19.49 7.25 2.54 14.12 1 10.03 6.38 0.14 2.02 150.13 4.98 0.16 3.49 0.29 5.95 16.58 5.77 0.53 27.04 2.67 8.11 8.22 3.51 1.06 7.95 1.16 6.68 16.32 e Std3 Dev (Ppb) 0.10 0.14 0.34 0.19 0.05 0.04 0.30 2.40 0.08 0.01 0.04 2.09 0.10 0.01 0.08 0.01 0.19 0.33 0.08 0.01 0.61 0.02 0.08 0.11 0.04 0.01 0.10 0.01 0.09 0.27 A< Mean2 Cone (ppb) 0.52 1.33 1.03 0.54 0.60 1.06 1.66 1.53 - 1.89 0.81 0.65 0.77 1.12 1.10 1.07 1.53 1.04 1.28 1.05 I 1.79 | 0.87 I 0.98 1.31 1.24 0.91 1 1.02 0.88 0.95 1.09 jetaldehyd \bsoiute3 Percent Diff 5.83 4.51 0.98 31.78 33.33 23.70 3.02 * * 6.35 3.73 38.76 6.54 11.66 22.83 5.61 7.84 11.54 19.61 2.87 26.82 36.78 3.08 7.63 2.43 2.20 0.00 3.43 0.00 11.96 e Std3 Dev (ppb) 0.02 0.04 0.01 0.12 0.14 0.18 0.04 * * 0.08 0.02 0.18 0.04 0.09 0.18 0.04 0.08 0.00 0.18 0.02 0.34 0.23 1 0.02 | 0.07 0.02 0.01 0.00 0.02 0.00 0.08 Mean2 Cone (ppb) 0.54 1.53 1.52 1.31 0.96 1.36 0.88 0.74 0.55 1.12 1.62 1.06 0.97 0.56 0.86 2.91 3.15 1.91 1.19 1.04 1.48 0.75 I 0.71 0.93 0.92 1.11 1.07 0.83 1.10 1.19 Acetone Absolute3 Percent Diff 35.51 34.75 0.66 4.58 15.71 0.74 2.27 * 14.55 31.39 28.40 21.80 23.83 30.63 1.17 4.81 3.17 0.52 2.53 2.90 19.66 4.03 8.45 9.73 2.17 4.52 3.74 6.06 0.00 11.37 Std3 Dev (ppb) 0.13 0.37 0.01 0.04 0.11 0.01 0.01 * 0.06 0.25 0.33 | 0.16 0.16 0.12 0.01 0.10 0.07 0.01 0.02 0.02 0.21 0.02 0.04 0.06 0.01 0.04 0.03 0.04 0.00 0.09 ' In Case 1, mean concentrations are calculated using detected tube concentrations only. 2 '-" indicates concentration below analytical detection limit (ADL). ' "*" indicates insufficient data to perform calculation.------- TABLE B-16. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 21 Sauget, IL (SAIL) Sample Date 12-Mar-90 24-Mar-90 05-Apr-90 16-Apr-90 ll-May-90 23-May-90 04-Jun-90 16-Jun-90 ; 28-Jun-90 | 10-Jul-90 24-Jul-90 03-Aug-90 14-Aug-90 27-Aug-90 08-Sep-90 25-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 19-Nov-90 j Ol-Dec-90 !3-Dec-90 27-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 12-Feb-91 23-Feb-91 Week Day M St Th M F W M St ID Number 1165 1177 1195 1208 1226 1246 1262 1269 Formaldehyde Mean Cone (ppb) 1.16 1.52 2.16 1.39 0.97 1.97 3.05 3.09 Th | 1280 | 1.88 T T F T M St T T Sn F W M St I Th Th Sn F W T St 1294 1315 1329 1344 1354 1372 1401 1404 1419 1441 1461D 1471 1491D 1501 1523 1535 1552D 1565 1581 1604D Average 7.23 2.48 1.97 2.81 6.15 3.16 3.45 4.54 2.84 2.08 1.88 3.18 1.13 1.48 1.83 1.71 | 1.88 1.76 1.72 1.94 2.49 Absolute Percent Diff 12.07 13.16 22.22 19.49 7.25 2.54 14.12 110.03 Std Dev (ppb) 0.10 0.14 0.34 0.19 0.05 0.04 0.30 Acetaldehyde Mean Cone (ppb) 0.52 1.33 1.03 0.54 0.60 1.06 1.66 2.40 | 0.86 6.38 | 0.08 0.14 I 0.01 2.02 150.13 4.98 0.16 3.49 0.29 5.95 16.58 5.77 0.53 27.04 2.67 0.04 2.09 0.10 0.01 0.08 0.01 0.19 0.33 0.08 0.01 0.61 0.18 1.89 0.81 0.65 0.77 1.12 1.10 1.07 1.53 1.04 1.28 1.05 1.79 0.02 1 0.87 8.11 | 0.08 8.22 | 0.11 3.51 1.06 7.95 1.16 6.68 15.99 0.04 0.01 0.10 0.01 0.09 0.26 0.98 1.31 1.24 0.91 1.02 0.88 0.95 1.03 Absolute Percent Diff 5.83 4.51 0.98 31.78 33.33 23.70 3.02 157.89 0.00 6.35 3.73 38.76 6.54 11.66 22.83 5.61 7.84 11.54 19.61 2.87 26.82 Std Dev (ppb) 0.02 0.04 0.01 0.12 0.14 0.18 0.04 Acetone Mean Cone (ppb) 0.54 1.53 1.52 1.31 0.96 1.36 0.88 0.95 0.46 0.00 0.08 0.02 0.18 0.04 0.09 0.18 0.04 0.08 0.00 0.18 0.02 0.55 1.12 1.62 1.06 0.97 0.56 0.86 2.91 3.15 1.91 1.19 1.04 0.34 1.48 36.78 | 0.23 | 0.75 3.08 I 0.02 7.63 2.43 2.20 0.00 3.43 0.00 16.58 0.07 0.02 0.01 0.00 0.02 0.00 0.11 0.71 0.93 0.92 1.11 1.07 0.83 1.10 1.18 Absolute Percent Diff 35.51 34.75 0.66 4.58 15.71 0.74 2.27 121.74 14.55 31.39 28.40 21.80 23.83 30.63 1.17 4.81 3.17 0.52 2.53 2.90 19.66 Std Dev (ppb) 0.13 | 0.37 | 0.01 0.04 0.11 0.01 0.01 | 0.40 1 0.06 I 0.25 | 0.33 I 0.16 I 0.16 0.12 0.01 0.10 0.07 0.01 0.02 0.02 0.21 4.03 0.02 | 8.45 9.73 2.17 4.52 3.74 6.06 0.00 15.17 0.04 1 0.06 0.01 | 0.04 I 0.03 0.04 0.00 0.10 In Case 2, mean concentrations are calculated using half the analytical detection limit (ADL) for tube concentrations below ADL.------- TABLE B-17. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE I1 Toledo, OH (TLOH) Sample Date 05-Apr-90 16-Apr-90 29-Apr-90 ll-May-90 23-May-90 04-Jun-90 16-Jun-90 28-Jun-90 i 10-Jul-90 22-Jul-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 19-Nov-90 Ol-Dec-90 13-Dec-90 Week Day Th M Sn F W M St Th T Sn F W M St Th T Sn F W M St 1 Th ID Number 1193 1 1205D 1214 1223 1243 1253 1264 1278 1293 1306 1326 1345 1355 1367 1387 1410 1425 1440 1455 1478D | 1486 1507 Average Fo Mean* Cone (ppb) 1.88 1.43 1.53 1.22 1.73 0.79 3.17 2.02 3.46 1.56 4.19 4.90 5.43 2.36 1.35 2.67 2.06 1.89 1.60 3.45 | 2.05 2.04 2.40 rmaidehyc Absolute3 Percent Diff 13.83 28.77 5.90 1.64 16.81 10.13 66.03 3.47 0.29 5.13 12.89 0.41 3.50 18.64 23.70 2.25 6.80 17.99 6.90 2.03 10.73 | 6.39 12.01 & Std3 Dev (ppb) 0.18 0.29 0.06 0.01 0.21 0.06 1.48 0.05 0.01 0.06 0.38 0.01 0.13 0.31 0.23 0.04 0.10 0.24 0.08 0.05 0.16 1 0.09 0.19 A Mean3 Cone (ppb) 0.70 J 1.01 0.75 - 1.05 - 1.23 - 0.76 - 2.65 1.39 1.57 1.16 0.55 1 1.36 - 0.68 0.81 2.36 | 1.07 I 0.59 1.16 cetaldehyc Absolute3 Percent Diff 57.14 26.87 33.56 * 1.90 * 75.92 * 73.68 * 10.57 5.05 33.12 74.14 * 4.41 * * 2.47 15.71 10.33 * 30.35 \e Std3 Dev (ppb) 0.28 | 0.19 0.18 j * 0.01 * 0.66 * 0.40 * 0.20 0.05 0.37 0.61 * 0.04 * * 1 0.01 1 0.26 0.08 * 0.24 Mean2 Cone (ppb) 1.45 | 1.21 1.43 0.83 2.04 0.55 1.04 0.69 2.08 1.34 3.16 3.73 0.76 1.39 1.52 2.22 2.14 1.35 1.16 1 1.54 1 1.29 1.00 1.54 Acetone Absolute3 Percent Diff 2.76 2.49 17.54 15.76 21.57 10.91 68.60 5.80 16.87 16.42 14.90 14.23 10.53 5.76 8.58 4.97 0.47 2.96 7.79 1.95 9.30 9.05 12.24 Stds Dev (ppb) 0.03 | 0.02 1 0.18 0.09 0.31 0.04 0.50 0.03 1 0.25 1 0.16 0.33 0.37 | 0.06 0.06 0.09 0.08 0.01 0.03 0.06 0.02 1 0.08 | 0.06 0.13 ' In Case 1, mean concentrations are calculated using detected tube concentrations only. : "-" indicates concentration below analytical detection limit (ADL). J "*" indicates insufficient data to perform calculation.------- TABLE B-18. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 21 Toledo, OH (TLOH) Sample Date 05-Apr-90 16-Apr-90 29-Apr-90 1 l-May-90 23-Mav-90 04-Jun-90 16-Jun-90 28-Jun-90 Week Day Th M Sn F W M St Th j 10-Jul-90 1 T 22-Jul-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 Sn F W M St Th T Sn F W 19-Nov-90 | M Ol-Dec-90 | St 13-Dec-90 1 Th ID Number 1193 1205D 1214 1223 1243 1253 1264 1278 1293 Formaldehyde Mean Cone (ppb) 1.88 1.43 1.53 1.22 1.73 0.79 3.17 2.02 3.46 1306 | 1.56 1326 4.19 1345 1355 1367 1387 1410 1425 1440 1455 1478D 1486 1507 Average 4.90 5.43 2.36 1.35 2.67 2.06 1.89 1.60 3.45 2.05 2.04 2.40 Absolute Percent Diff 13.83 1 28.77 5.90 1.64 16.81 10.13 66.03 3.47 0.29 5.13 12.89 0.41 3.50 18.64 23.70 2.25 6.80 17.99 6.90 | 2.03 I 10.73 i 6.39 12.01 Std Dev (ppb) 0.18 0.29 0.06 0.01 0.21 0.06 1.48 0.05 Acetaidehyde Mean Cone (ppb) 0.70 1.01 0.75 0.18 1.05 0.18 1.23 Absolute Percent Diff 57.14 26.87 33.56 0.00 1.90 0.00 75.92 0.18 0.00 0.01 | 0.76 0.06 0.38 0.01 0.13 0.31 ! 0.23 I 0.04 | 0.10 | 0.24 | 0.08 1 0.05 1 0.16 1 0.09 0.19 Std Dev (ppb) 0.28 0.19 0.18 0.00 0.01 0.00 0.66 0.00 Acetone Mean Cone (ppb) 1.45 1.21 1.43 0.83 2.04. 0.55 1.04- 0.69 73.68 0.40 i 2.08 0.18 0.00 2.65 10.57 |_ 1.39 5.05 1.57 33.12 1.16 0.37 1.36 0.18 0.43 0.81 2.36 1.07 | 0.39 0.91 74.14 101.37 4.41 0.00 116.28 2.47 15.71 10.33 106.49 34.05 0.00 0.20 0.05 0.37 0.61 0.26 0.04 0.00 0.00 0.01 0.26 0.08 0.29 0.18 1.34 3.16 3.73 0.76 1.39 1.52 2.22 2.14 1.35 1.16 ]_1.54 | 1.29 Absolute Percent Diff 2.76 2.49 17.54 15.76 21.57 10.91 68.60 5.80 16.87 16.42 14.90 14.23 10.53 5.76 8.58 4.97 0.47 2.96 7.79 1.95 9.30 1.00 1 9.05 1.54 L2.24 Std Dev (ppb) 0.03 I 0.02 0.18 0.09 0.31 0.04 0.50 0.03 1 0.25 1 0.16 I 0.33 | 0.37 0.06 0.06 0.09 0.08 0.01 0.03 0.06 0.02 0.08 | 0.06 1 0.13 In Case 2, mean concentrations are calculated using half the analytical detection limit (ADL) for tube concentrations below ADL.------- TABLE B-19. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 1' Washington, DC (W1DC) Sample Date i2-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 ll-May-90 Week Day M St Th T Sn F 23-May-90 1 W 04-Jun-90 I M j 16-Jun-90 | St 1 28-Jun-90 | Th 10-Jul-90 T 22-Jul-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 2Q-Sep-90 02-Oct-90 14-Oct-90 Sn 1 F W M St Th T Sn 26-Oct-90 | F 07-Nov-90 j W ! 19-Nov-90 | M Ol-Dec-90 13-Dec-90 25-Dec-90 St Th T 06-Jan-9L | Sn 18-Jan-91 | F 30-Jan-91 ll-Feb-91 23-Feb-91 1 w M St ID Number 1171 1179 1188 1203D 1220 1233 1249 Formaldehyde Mean2 Cone (ppb) 3.85 2.34 3.75 3.62 I 3.61 | 1.90 \bsoiute3 Percent Diff 46.55 61.24] 53.67 ! 4.42 14.15] 70.18 Stds Dev (ppb) 1.27 1.01 1.42 0.11 0.36 Acetaidehyde Mean2 Cone (ppb) 1.37 1.73 1.54 0.67 1.38 0.94 0.69 2.84 j 32.10 I 0.64 1258 | 2.11 | 30.88 1 0.46 0.93 0.66 1265 | 9.49 | 5.48 I 0.37 | 3.57 1284 | 9.88 | 6.28 | 0.44 | 2.77 1295 1309 1322 1340 1360 1379 1385 1411 1430 1442 1457 9.38 8.10 8.36 8.61 7.55 3.89 11.30| 0.751 2.40 2.84 1 0.16 i 1.83 2.63 7.09 30.09 6.44 3.69 2.71 4.13 3.85 2.72 3.70 5.33 2.34 7.00 5.95 0.16 0.43 1.61 0.18 0.07 0.16 3.04 2.70 2.25 1.05 1.21 1.34 0.06 1.35 0.13 | 1.23 I 0.16 | 1.59 1480D i 4.40 | 1.82 I 0.06 j 1.64 1485 1503 1520 1528 1550 1566 1588D 1595 Average 7.48 0.13 4.43 3.96 3.71 2.11 5.47 3.07 3.82 4.86 | 4.29 0.01 | 2.62 0.13 5.82 0.16 0.00 0.48 3.48 5.86 4.19 14.49 | 0.00 I 0.01 0.13 0.13 0.11 0.39 1.94 1.76 2.06 1.02 2.07 1.15 1.52 1.70 Absolute3 Percent Diff 59.85 41.62 31.92 46.62 3.64 Std3 Dev (ppb) 0.58 0.51 0.35 0.22 0.04 62.77 0.30 Acetone Mean1 Cone (ppb) 2.89 1.49 1.53 2.26 1 1.59 1.01 Absolute3 Percent Diff 13.84 45.64 48.37 11.09 13.84 55.45 43.85 i 0.29 1.12 | 17.86 Std3 Dev (ppb) 0.28 0.48 0.52 0.18 | 0.16 0.40 0.14 29.01 0.13 i 0.98 1 42.86 | 0.30 | 15.13 1 0.38 i 2.90 | 34.48 ( 0.71 1 5.42 1 0.11 | 2.68 1.25 15.30 5.26 11.50 8.46 10.53 33.06 1.49 8.18 8.98 4.42 0.02 0.20 0.11 0.22 0.13 0.08 0.28 0.00 0.08 0.08 1.97 1.86 3.59 2.90 2.53 1.34 2.30 2.00 1.12 1.29 0.05 1.60 3.06 I 0.04 1 1.25 0.00 | 0.00 | 1.89 1.55 | 0.02 1.35 3.99 1.46 5.88 0.97 6.11 2.63 15.80 0.05 1.06 0.02 i 1.68 0.04 | 0.81 0.01 0.05 0.03 0.15 1.75 28.04 30.89 9.68 57.94 15.54 17.39 13.43 6.54 1.00 13.45 5.45 12.50 20.80 14.32 65.19 11.32 13.73 9.88 12.03 0.80 13.84 1.15 1.75 2.62 21.97 0.53 I 0.43 0.13 1.47 0.32 0.31 0.13 0.11 0.01 0.11 0.05 1 0.14 i 1 0.18 | i 0.19 j 0.62 0.08 0.16 0.06 0.15 0.08 0.02 0.28 In Case 1, mean concentrations are calculated using detected tube concentrations only. •-" indicates concentration below analytical detection limit (ADL). "*' indicates insufficient data to perform calculation.------- TABLE B-20. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 2' Washington, DC (W1DC) Sample Date 12-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 Week Day M St Th T 29-Apr-90 Sn ll-May-90 F 23-May-90 W ID Number Formaldehyde Mean Cone (ppb) 1171 3.85 1179 1188 1203D 1220 1233 2.34 3.75 3.62 3.61 1.90 1249 2.84 Absolute Percent Diff Std Dev (ppb) 46.55 | 1.27 61.24 1.01 53.67 4.42 14.15 1.42 0.11 0.36 70.18 1 0.94 32.10 | 0.64 Acetaldehyde Acetone Mean Cone (ppb) 1.37 1.73_[ 1.54 0.67 1.38 0.69 0.93 Absolute Percent Diff Std Dev (Ppb) Mean Cone; (ppb) 59.85 1 0.58 1 2.89 41.62 31.92 46.62 3.64 62.77 0.51 1.49 0.35 1.53 0.22 ! 2.26 0.04 0.30 Absolute Percent Diff 13.84 45.64 48.37 Std Dev (Ppb) 0.28 0.48 0.52 11.09 i 0.18 1.59 13.84 1.01 0.16 55.45 0.40 | 43.85 0.29 1.12 17.86 0.14 i 04-Jun-90 M 1258 2.11 30.88 ! 0.46 i 0.66 29.01 0.13 0.98 42.86 0.30 1 16-Jun-90 St 1265 9.49 5.48 1 0.37 | 3.57 15.13 0.38 2.90 34.48 0.71 28-Jun-90 Th | 1284 1 9.881 6.28 0.44 | 2.77 5.42^ 0.11 2.68 28.04 j_ 0.53 | 10-Jul-90 T 1295 22-Jul-90 | Sn 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-0ct-90 14-0ct-90 26-Oct-90 07-Nov-90 F W M St Th T Sn F W 1309 1322 1340 9.38 8.10 8.36 8.61 1360 | 7.55 1379 1385 1411 1430 1442 3.89 3.69 4.13 3.85 2.72 1457 ! 3.70 11.301 0.75 2.40 1.25 2.841 0.16 2.63 7.09 30.09 6.44 2.71 5.33 2.34 0.16 0.43 1.61 0.18 0.07 0.16 0.06 7.00| 0.13 5.95 0.16 I9-Nov-90 M 1480D 1 4.40 1.82 0.06 L01-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 J_ St 1485 7.48 0.13 | 0.01 Th T Sn F W ll-Feb-91 | M 23-Feb-91 St 1503 1520 1528 1550 1566 1588D 1595 Average 4.43 3.96 3.71 2.11 5.47 3.07 3.82 4.86 4.29 5.82 0.00 0.48 3.48 5.86 4.19 14.49 0.13 0.16 0.00 0.01 0.13 0.13 0.11 0.39 1.83 15.30 3.04 2.70 2.25 1.05 1.21 1.34 1.35 1.23 1.59 5.26 J 11.50 8.46 10.53 33.06 1.49 8.18 8.98 4.42 0.02 1.97 30.89 0.43 0.20 1.86 9.68 0.13 0.1 Ij^ 3.59 0.22 2.90 0.13 0.08 0.28 0.00 0.08 0.08 2.53J [ 1.34 2.30 2.00 57.94 15.54 17.39 13.43 6.54 1.00 1.12 | 13.45 1.29 i 5.45 0.05 | 1.60 I 12.50 1.64 3.06 0.04 1.25 1 20.80 2.62 1.94 1.76 2.06 1.02 2.07 1.15 1.52 1.70 0.00 I 0.00 1.89 1 14.32 1.55 3.99 1.46 5.88 0.97 6.11 2.63 15.80 0.02 1.35 0.05 1.06 0.02 1.68 0.04 0.01 0.05 0.03 0.15 0.81 1.75 65.19 11.32 13.73 9.88 12.03 0.80 | 13.84 1.15 1.75 1.47 0.32 0.31 0.13 0.11 0.01 0.11 0.05 0.14 0.18 0.19 I 0.62 0.08 0.16 0.06 0.15 0.08 2.62 | 0.02 21.97 0.28 In Case 2, mean concentrations are calculated using half the analytical detection limit (ADL) for tube concentrations below ADL.------- TABLE B-21. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE I1 Wichita, KS (W1KS) Sample Date 13-Mar-90 25-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 ll-May-90 23-May-90 04-Jun-90 16-Jun-90 28-Jun-90 10-Jul-90 22-Jul-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-0ct-90 26-Oct-90 07-Nov-90 l9-Nov-90 Week Day T Sn Th T Sn F W M St Th T Sn F W M St Th T Sn F W M Ol-Dec-90 | St 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 Th T Sn F W M St ED Number 1173 1176 1198D 1209 1218 1227 1248 1254 1272 1287 1296 1311 1333 1342 1362 1370 1395 1412 1428 1439 1459D 1468 1487 1511 1515D 1536 1549 1560D 1578 1603 Average Formaldehyde Mean1 Cone (ppb) 1.38 3.96 2.18 3.75 4.16 2.45 3.72 3.22 Absolute3 Percent Diff 1.45 4.80 7.34 11.48 10.58 1.63 4.04 Stds Dev (ppb) 0.01 0.13 0.11 0.30 0.31 0.03 0.11 0.62 i 0.01 6.37 I 7.22 0.33 7.28 7.90 2.79 5.03 4.58 8.95 6.78 4.58 4.91 4.78 0.14 1.01 6.45 21.07 10.48 11.62 0.74 4.80 0.81 3.14 6.08 | 0.82 2.63 2.67 4.13 | 4.61 3.42 2.56 5.41 3.46 7.39 5.94 7.43 4.60 4.73 5.26 3.91 0.56 0.87 0.68 3.03 1.35 3.91 4.57 0.01 0.06 0.13 0.75 0.34 0.74 0.04 0.16 0.03 0.11 0.04 0.05 0.13 0.13 0.07 0.02 0.02 0.04 0.13 0.07 0.13 0.15 Acetaldebyde Mean2 Cone (ppb) 0.40 2.48 1.58 0.85 2.04 0.69 1.42 1.29 1.92 2.14 2.95 0.97 2.36 1.68 2.20 2.65 1.97 1.58 2.26 2.11 1.30 2.18 1.71 1.12 2.64 1.48 3.53 2.11 2.68 1.54 1.86 Absolute3 Percent Diff * 1.21 0.63 61.18 6.86 18.98 16.90 24.81 Std3 Dev (ppb) * 0.02 0.01 0.37 0.10 0.09 0.17 Acetone Mean* Cone (ppb) 0.96 2.04 1.49 1.47 1.97 1.50 1.57 0.23 1.44 10.42 1 0.14 7.96 13.92 6.19 33.90 5.95 8.66 7.18 5.60 2.53 11.50 8.53 2.32 5.50 9.97 16.07 4.93 1.35 3.40 10.43 0.37 7.79 10.86 0.12 0.29 0.75 2.16 2.51 0.04 | 1.57 0.57 0.07 0.13 0.13 0.08 0.00 0.18 0.13 0.02 0.78 1.31 2.23 4.01 1.93 3.72 2.73 3.83 1.41 0.08 1.75 0.12 0.13 0.09 0.01 0.08 0.16 0.01 0.08 0.13 1.47 0.86 1.43 1.16 3.15 1.31 3.52 1.67 1.92 Absolute3 Percent Diff 54.17 45.70 6.06 9.52 4.06 6.02 7.03 44.44 55.03 55.56 2.39 19.11 11.61 * 9.44 1.75 5.18 4.58 2.20 1.31 10.68 1.14 1.36 0.00 3.51 7.79 1.90 2.30 0.57 4.20 13.06 Std1 Dev (ppb) 0.37 0.66 0.06 0.10 0.06 0.06 0.08 0.45 0.29 0.85 0.04 0.21 0.06 * 0.15 0.05 0.07 0.12 0.04 0.04 0.11 0.01 0.01 0.00 0.04 0.06 0.04 0.02 0.01 0.05 0.14 ' In Case 1, mean concentrations are calculated using detected tube concentrations only. 2 "-" indicates concentration below analytical detection limit (AOL). 3 "*" indicates insufficient data to perform calculation.------- TABLE B-22. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE AND STANDARD DEVIATION FOR CASE 2' Wichita, KS (W1KS) Sample Date 13-Mar-90 25-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 ll-May-90 23-May-90 ! 04-Jun-90 : 16-Jun-90 L_28-Jun-90 10-Jul-90 22-Jul-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 ! 19-Nov-90 Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 Week Day T Sn Th T Sa F W M ID Number 1173 1176 1198D 1209 1218 1227 1248 1254 Formaldehyde Mean Cone (ppb) 1.38 3.96 2.18 3.75 4.16 2.45 3.72 3.22 Absolute Percent Diff 1.45 4.80 | 7.34 11.48 10.58 1.63 4.04 0.62 Std Dev (ppb) 0.01 0.13 0.11 0.30 0.31 0.03 0.11 0.01 St 1272 1 6.37 ! 7.22 0.33 Th T Sn F W M St Th T Sn F W 1287 7.28 0.14 0.01 1296 7.90 | 1.01 | 0.06 1311 1333 1342 1362 1370 1395 1412 1428 1439 1459D 2.79 5.03 4.58 8.95 6.78 4.58 4.91 4.78 6.08 I 2.63 M 1 1468 4.13 St Th T Sn F W M St 1487 | 3.42 1511 1515D 1536 1549 1560D 1578 1603 Average 2.56 5.41 3.46 | 7.39 5.94 7.43 4.60 4.73 6.45 | 0.13 21.07 10.48 11.62 0.74 4.80 0.81 3.14 0.82 2.67 I 4.61 5.26 3.91 0.56 0.87 0.68 3.03 1.35 3.91 4.57 0.75 0.34 0.74 0.04 0.16 0.03 0.11 0.04 0.05 1 0.13 0.13 0.07 0.02 0.02 0.04 0.13 0.07 0.13 0.15 Acetaidehyde Mean Cone (ppb) 0.29 2.48 1.58 0.85 2.04 0.69 1.42 1.29 I 1.92 2.14 2.95 0.97 2.36 1.68 2.20 2.65 1.97 1.58 2.26 2.11 1.30 2.18 1.71 1.12 2.64 1.48 3.53 2.U 2.68 1.54 1.86 Absolute Percent Diff 75.86 1.21 0.63 61.18 6.86 18.98 | 16.90 24.81 10.42 7.96 13.92 6.19 33.90 5.95 8.66 7.18 5.60 2.53 11.50 8.53 2.32 Std Dev (ppb) 0.16 0.02 0.01 0.37 0.10 0.09 0.17 0.23 Acetone Mean Cone (ppb) 0.96_l 2.04 | 1.49 1.47 1.97 1.50 1.57 Absolute Percent Diff 54.17 45.70 | Std Dev (ppb) 0.37 | 0.66 | 6.06 | 0.06 9.52 4.06 6.02 | 7.03 0.10 0.06 0.06 0.08 1 1.44. ( 44.44 j 0.45 1 0.14 I 0.75 | 55.03 I 0.29 1 0.12 0.29 2.16 2.51 0.04 i 1.57 0.57 | 0.78 0.07 0.13 0.13 0.08 0.00 0.18 0.13 0.02 0.75 2.23 4.01 1.93 3.72 2.73 3.83 1.41 5.50 0.08 | 1.75 9.97 16.07 4.93 1.35 3.40 10.43 0.37 7.79 13.03 0.12 0.13 0.09 0.01 0.08 0.16 0.01 0.08 0.13 1.47 0.86 1.43 1.16 j 3.15 1.31 3.52 1.67 1.90 55.56 | 0.85 | 2.39 | 0.04 1 19.11 11.61 0.21 I 0.06 151.68 ! 0.80 9.44 1.75 5.18 4.58 2.20 1.31 0.15 0.05 0.07 0.12 0.04 0.04 | 10.68 1 0.11 | 1.14 j 0.01 | 1.36 0.00 3.51 7.79 1.90 1 0.01 | 0.00 0.04 j 0.06 0.04 2.30 0.02 0.57 | 0.01 4.20 | 0.05 17.68 0.16 In Case 2. mean concentrations arc calculated using half the analytical detection limit (ADL) for tube concentrations below ADL.------- TABLE B-23. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE I1 Washington, DC (W2DC) Sample Date 12-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 ll-May-90 23-May-90 04-Jun-90 16-Jun-90 28-Jun-90 10-Jul-90 22-Jul-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 19-Nov-90 Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 Week Day M St Th T Sn F W ID Number 1172 1181 1191 1199 1217D 1234 Formaldehyde Mean1 Cone (ppb) 10.04 5.22 6.13 6.28 4.44 3.45 1247 4.76 M ] 1259 2.95 St 1266 10.36 Th 1283 13.32 T 1292 Sn 1312 F W M St Th T Sn F W M St Th T Sn F W M St 1325 1336 1356 1378 1389 1408 1429 1443 1456 1473 1489D 1506 11.14 8.62 12.28 10.77 8.77 5.56 6.24 7.59 5.70 7.86 Absolute3 Percent Diff 69.46 68.84 Std3 Dev (Ppb) 4.93 2.54 29.88 | 1.29 45.54 5.19 41.16 37.39 48.14 2.02 0.16 1.00 1.26 Acetaldehyde Mean3 Cone (ppb) 4.89 2.50 2.29 2.39 1.79 1.04 1.38 1.00 1.38 3.28 0.24 4.46 1.73 14.46 9.40 10.02 18.57 14.26 0.90 3.05 3.82 11.93 12.60 8.99 1 6.57 0.16 1.14 0.57 0.87 1.41 0.88 0.04 0.13 0.21 0.48 0.70 0.42 3.82 3.60 2.30 4.00 3.23 2.70 1.76 2.46 2.03 2.62 1.53 1.99 10.43 2.68 0.20 2.76 9.40 I 1.49 j 0.10 9.88 1518 9.63 1529D | 6.23 1551 1568D 1583 1599D Average 9.37 10.09 4.64 7.53 7.92 16.10 3.12 4.98 2.03 1.88 7.76 1.06 16.58 1.12 0.21 0.00 0.13 0.13 0.25 0.06 0.79 3.10 2.50 1.80 2.56 1.69 2.82 1.50 1.44 2.47 Absolute3 Percent Diff 67.76 84.57 18.82 78.41 Std3 Dev (ppb) 2.34 1.49 0.30 1.32 8.40 0.11 62.80 0.46 26.09 38.55 Acetone Mean3 Cone (ppb) 5.24 1.84 2.12 2.90 2.21 1.31 0.25 1.58 0.37 1.10 Absolute3 Percent Diff 62.08 99.73 32.62 StdJ Dev (ppb) 2.30 1.29 0.49 60.45 I 1.24 41.63 1 0.65 60.54 i 0.56 6.33 | 0.07 34.55 I 0.27 | 22.42 0.71 3.78 8.74 1 0.23 6.03 0.16 4.51 24.64 0.78 13.63 0.35 2.27 5.66 0.09 2.07 0.50 0.00 1.11 5.13 4.48 6.90 21.80 3.28 3.51 0.01 | 4.99 0.00 0.02 0.06 0.08 0.00 0.40 0.04 0.05 3.28 2.61 1.86 2.90 2.72 1.36 1.30 23.79 | 0.38 9.20 | 0.13 | 29.26 | 1.03 24.73 1.92 3.23 8.28 3.68 20.59 11.58 0.57 0.04 0.04 0.17 0.07 0.20 0.11 3.38 1 9.19 I 0.22 8.70 0.17 1.98 19.75 0.28 3.55 0.08 | 2.59 10.02 0.18 1.67 12.50 2.37 5.67 3.34 1.39 17.64 0.02 0.23 0.03 0.11 0.04 0.01 0.32 2.07 1.01 1.71 1.30 4.03 1.08 0.92 2.40 1.16 | 0.02 J_ 19.85 | 0.29 18.91 0.00 19.31 28.57 13.95 4.35 23.42 0.13 0.00 0.18 | 0.81 0.11 0.03 0.42 In Case 1, mean concentrations are calculated using detected tube concentrations only. "-" indicates concentration below analytical detection limit (ADL). "*" indicates insufficient data to perform calculation.------- TABLE B-24. SUMMARY OF MEAN CONCENTRATION, ABSOLUTE PERCENT DIFFERENCE, AND STANDARD DEVIATION FOR CASE 2' Washington, DC (W2DC) Sample Date 12-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 ll-May-90 23-May-90 04-Jun-90 Week Day M St Th T Sn F W M 16-Jun-90 | St 28-Jun-90 10-Jul-90 22-Jul-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 Th T Sn F W M St Th T Sn F 07-Nov-90 j W 19-Nov-90 | M Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 1 St Th T Sn F W M St ED Number 1172 1181 1191 1199 1217D 1234 1247 1259 Formaldehyde Mean Cone (ppb) 10.04 | 5.22 6.13 6.28 4.44 3.45 4.76 2.95 Absolute Percent Diff 69.46 Std Dev (ppb) 4.93 68.84 i 2.54 Acetaldehyde Mean Cone (PPb) 4.89 2.50 29.88 | 1.29 2.29 45.54 I 2.02 5.19 | 41.16 | 37.39 48.14 0.16 1.00 1.26 2.39 1.79 1.04 1.38 1.00 1 1.38 1266 ! 10.36 | 3.28 ! 0.24 I 4.46 1283 1292 13.32 11.14 1312 8.62 1325 1336 1356 1378 1389 1408 1429 1443 1456 1473 1489D 1506 1518 1529D 1551 1568D 1583 1599D Average 12.28 10.77 8.77 5.56 6.24 7.59 5.70 7.86 8.99 1.73 | 0.16 14.46 Absolute Percent Diff 67.76 84.57 18.82 78.41 | Std Dev (ppb) 2.34 1.49 0.30 1.32 8.40 | 0.11 62.80 1 0.46 26.09 | 0.25 38.55 I 0.37 22.42 | 0.71 Acetone Mean Cone (ppb) 5.24 1.84 2.12 2.90 2.21 1.31 1.58 1.10 3.78 3.82 I 6.03 i 0.16 | 4.51 1.14 3.60 9.40 j 0.57 2.30 10.02 18.57 14.26 0.90 3.05 3.82 11.93 0.87 1.41 0.88 0.04 0.13 0.21 0.48 4.00 3.23 2.70 1.76 2.46 2.03 2.62 12.60 | 0.70 | 1.53 13.63 | 0.35 5.66 I 0.09 0.50 | 0.01 0.00 1.11 5.13 4.48 6.90 21.80 3.28 6.57 | 0.42 1 1.99 | 3.51 10.43 | 2.68 I 0.20 1 2.76 | 8.70 9.40 9.88 9.63 6.23 9.37 10.09 4.64 7.53 7.92 1 1.49 | 0.10 | 3.10 16.10 3.12 4.98 2.03 1 1.88 1.12 0.21 | 0.00 0.13 0.13 7.76 | 0.25 1.06 16.58 2.50 1.80 2,56 1.69 2.82 1.50 | 0.06 | 1.44 0.79 2.47 3.55 10.02 1.67 12.50 2.37 5.67 3.34 1.39 17.64 0.00 0.02 0.06 0.08 0.00 0.40 0.04 0.05 2.27 2.07 4.99 3.28 2.61 1.86 2.90 2.72 1.36 1.30 3.38 Absolute Percent Diff 62.08 99.73 32.62 60.45 41.63 60.54 6.33 34.55 8.74 24.64 23.79 9.20 29.26 24.73 1.92 3.23 8.28 3.68 20.59 11.58 9.19 0.17 | 1.98 | 19.75 0.08 0.18 0.02 0.23 0.03 0.11 0.04 0.01 0.32 2.59 2.07 1.01 1.71 1.30 4.03 1.08 0.92 2.40 I 1.16 19.85 18.91 0.00 19.31 28.57 13.95 4.35 23.42 Std Dev (Ppb) 2.30 1.29 0.49 1.24 0.65 0.56 0.07 0.27 0.23 | 0.78 0.38 0.13 1.03 0.57 0.04 0.04 0.17 0.07 0.20 0.11 0.22 1 0.28 1 0.02 | 0.29 0.13 0.00 | 0.18 0.81 0.11 0.03 0.42 In Case 2, mean concentrations are calculated using half the analytical detection limit (ADL) for tube concentrations below ADL.------- Appendix C - Analytical Data Listing :32-045/can.20ef CarOonvi 1990 Final Reoort------- TABLE C-l. SUMMARY OF CONCENTRATION AND PURITY FOR BRLA Sample Date Week Day 10-Jul-90 T 16-Jul-90 22-Jul-90 28-M-90 03-Aug-90 09-Aug-90 15-Aug-90 21-Aue-90 27-Aug-90 02-Sep-90 08-Seo-90 M Sn St F Th W T M Sn St i 14-Seo-90 F 20-Sw>-90 Th 26-Sep-90 02-0ct-90 08-Oct-90 14-Oct-90 20-Oct-90 26-Oct-90 Ol-Nov-90 07-Nov-90 19-Nov-90 Ol-Dec-90 13-Dec-90 25-Dcc-90 06-Jan-91 18-Jan-91 30-Jan-91 12-Feb-91 23-Feb-91 W T M Sn St F Th W M St Th T Sn F W F T ID Number Lot Formaldehyde Tube I (ppb) Tube 2 (ppb) Tubel Purity Tube 2 Purity Acetaldehyde Tubel (PI*) 1297 51 4.96 5.56 | 0.980 0.998 0.99 1303 1304 1317 1321 1331 1338 1347 1358 1365 1380 1382 55 55 55 55 55 55 55 55 55 55 55 1394 55 1396 1409 1417 1427 1433D 1445 1447 1453 1476D 1493 1497D 55 55 55 51 55 51 55 56 49 49 49 1512 60 1534 | 60 1556 1562D 1584D 1594 60 60 60 4.41 3.19 6.31 3.92 6.06 6.58 6.01 3.99 2.73 4.27 0.999 0.998 1.81 7.17 4.73 6.19 6.59 7.65 3.21 0.988 I 0.978 0.999 0.997 0.998 0.999 0.998 0.999 0.998 0.997 0.998 0.995 1.000 0.999 2.38 -999 -999 -999 2.11 2.24 -999 -999 2.50 0.976 0.996 -999 3.18 2.29 0.997 0.999 -999 3.87 3.57 0.983 0.992 -999 5.29 11.02 5.37 3.82 6.53 5.84 4.89 6.13 6.45 6.64 4.33 3.60 5.20 10.93 5.49 3.85 6.55 5.42 4.91 6.18 6.57 6.93 4.14 3.84 6.13 | 6.07 2.00 1 2.36 2.82 | 2.78 2.70 | 2.29 6.98 | 6.83 1.000 1.000 1.29 1.000 1.000 1.000 1.000 1.000 1.000 1.000 0.999 1.000 1.000 1.000 0.999 0.999 1.000 0.998 1.000 0.999 1.000 1.000 1.000 1.000 0.999 1.000 1.000 1.000 0.999 0.998 1.000 1.000 0.999 0.999 0.999 62 3.85 | 4.04 i 0.999 0.999 7.32 2.19 1.39 3.91 3.32 3.86 3.54 3.22 3.47 1.61 -999 2.19 1.00 1.23 1.52 3.71 1.79 Tube 2 (PI*) 1.07 1.77 -999 -999 -999 2.45 2.35 1.18 -999 -999 -999 Tubel Purity 0.993 0.996 0.000 0.859 0.773 0.987 0.977 0.975 0.796 0.667 0.795 Tube 2 Purity 0.995 1 0.992 | 0.765 | 0.906 I 0.742 0.990 0.978 0.958 0.647 0.974 0.000 -999 I 0.981 I 0.959 1.50 7.16 2.25 1.47 3.93 3.08 3.53 3.54 3.14 4.45 1.05 -999 2.32 1.29 1.37 1.08 3.62 1.69 0.993 0.992 0.992 0.992 0.993 0.992 0.992 0.990 0.992 0.992 0.991 0.991 0.991 0.992 0.992 0.991 0.993 0.991 0.992 0.992 0.992 0.993 0.992 0.990 0.991 I 0.993 0.992 | 0.992 0.991 0.992 0.992 0.992 0.992 0.991 0.992 0.993 Acetone Tubel (ppb) -999 -999 -999 -999 -999 3.48 -999 -999 -999 -999 -999 -9991 -999 7.05 0.76 -999 3.45 4.54 2.70 4.73 3.43 3.18 0.86 -999 1.41 1.18 1.69 1.75 4.11 1.51 Tube 2 (Ppb) -999 -999 -999 -999 -999 3.28 -999 -999 -999 Tubel Purity 0.814 0.741 0.000 0.000 0.000 0.975 0.856 0.732 0.000 -999 0.000 -999 0.000 Tube 2 Purity 0.783 1 0.795 1 0.721 | O.OOOJ 0.000 | 0.989 0.909 0.000 0.000 0.000 0.000 -999 0.478 0.807 1 -999 7.34 0.88 -999 3.46 4.15 2.67 5.02 3.47 2.72 1.24 -999 0.667 |0.982 0.978 0.801 0.980 0.974 0.965 0.678 0.980 0.980 0.938 0.983 1.30 0.984 1.30 0.980 1.71 1.45 4.00 1.54 0.985 0.978 0.984 0.984 0.000 0.984 0.945 0.910 0.979 0.973 0.981 0.980 0.978 0.976 0.971 0.980 0.971 0.968 0.985 0.982 0.984 0.966 "-999.00" indicates concentration below analytical detection limit (ADL).------- TABLE C-2. SUMMARY OF CONCENTRATION AND PURITY FOR C4IL 1 Sample Date Week Day 24-Mar-90 1 St 05-Apr-90 | Th | 17-Apr-90 1 29-Apr-90 ll-May-90 23-Mav-90 04-Jun-90 16-Jun-90 28-Jun-90 T Sn F W M St Th 22-Jul-90 | Sn 03-Aue-90 j F j 16-Aug-90 Th i 27-Aua-90 1 M 08-Sep-90 20-Sep-90 02-0ct-90 14-Oct-90 26-Oct-90 08-Nov-90 19-Nov-90 OI-Dec-90 13-Dec-91 28-Dec-90 04-Jan-91 St Th T Sn F Th M St Th F I F I8-Jan-9I | F | 30-Jan-91 | W ll-Feb-91 23-Feb-91 | M St ID Number 1175 1196 1207 1219 1223 1244 1261 1268 1285 1314 1324 Lot 46 46 46 51 51 51 51 51 51 55 55 1343 | 55 1352 1375 1391 1407 1421 1436 1452 1475 1483 1504 1525 1537D 1547 55 55 55 55 51 51 56 49 49 49 60 60 60 1557 | 60 1577 1593 60 62 Formaldehyde Tubel (Ppb) 3.72 3.80 3.71 2.86 3.26 3.36 2.45 7.72 5.63 7.47 12.53 5.30 8.02 5.12 4.45 4.91 4.39 4.41 3.98 3.61 4.47 3.57 3.25 4.57 3.85 1 5.19 3.52 3.14 Tube 2 (Pf*) 3.96 4.29 4.06 Tubel Purity Tube 2 Purity Acctaldchydc j Acetone 1 Tubel (PI*) 0.997 I 0.925 1 2.61 0.993 I 0.994 I 2.88 0.999 3.49 2.74 2.44 7.28 5.95 7.72 14.75 0.994 0.949 0.989 0.983 0.890 0.999 0.999 0.999 0.998 0.996 0.991 0.989 0.997 0.997 0.999 0.998 1 0.996 5.05 | 1.000 6.84 5.38 5.39 5.26 4.79 4.26 4.04 4.14 3.25 3.39 3.21 4.66 0.999 1.71 | 1.53 1.04 1.76 1.51 0.94 3.54 2.55 2.96 4.02 Tube 2 (PI*) 2.56 1.92 1.82 1.31 1.75 1.48 0.91 3.26 2.38 3.03 5.64 Tube 1 Purity 0.887 0.981 0.995 0.601 0.983 0.997 0.994 0.991 0.534 0.995 0.947 Tube 2 Purity 0.992 1 0.995 | 0.994 | 0.953 0.894 0.994 Tube 1 (Ppb) 3.03 Tube 2 (PI*) 2.80 | 2.60 | 3.38 I 2.02 1 1.97 | 1.32 2.73 | 2.21 5.10 0.990 1 3.52 0.977 0.981 0.993 0.983 3.90 3.71 4.32 4.45 1.84 | 4.85 3.60 3.08 3.34 3.37 2.29 1.75 I 1.94 | 0.990 i 0.992 | 4.01 j 3.50 0.999 i 0.998 | 2.04 0.999 1.000 1.000 0.999 1.000 1.000 1.000 1.000 0.999 '1.000 | 1.000 0.997 0.999 1.000 0.999 1.000 2.28 2.14 1.81 2.24 2.31 1.000 1.98 1.000 1.000 0.999 1.000 0.999 3.71 1 1.000 j 1.000 1.90 2.38 1.71 1.58 2.09 | 1.41 j 4.42 I 1.000 | 1.000 1 2.01 3.33 3.22 1.000 0.999 1 1.000 1.000 | 1.31 0.98 2.28 2.22 2.39 1.90 2.42 2.31 1.90 2.23 1.39 1.09 1.57 2.07 i 1.38 | 2.04 | 1.32 ) 1.01 0.992 | 0.966 1 3.23 | 3.00 0.999 0.992 0.993 0.992 0.992 0.992 0.991 0.992 0.993 0.992 0.993 0.993 0.993 0.993 0.992 0.997 2.12 1.93 0.992 1 7.2.7 | 8.37 0.992 0.993 6.80 | 7.12 2.96 0.991 | 3.74 0.992 0.993 0.993 0.992 0.993 0.993 0.993 | 3.94 2.28 2.10 1.01 1.28 1.24 I 1 .45 2.95 3.31 3.94 2.65 1.86 0.98 1.18 1.24 1.19 0.992 I 1.74J 1.79 0.992 | 0.97 | 0.91 0.992 | 0.82 0.84 Tubel Purity 0.893 0.998 | 0.904 0.516 0.977 0.986 0.607 0.794 0.569 0.816 0.941 0.996 0.990 0.919 Tube 2| Purity i 0.440 1 0.979 1 0.960 1 0.845 1 0.632 1 0.907 ! 0.970 1 0.818 ! 0.911 1 0.816 1 0.905 1 0.995 1 0.967 1 0.989 1 0.980 1 0.981 1 0.984 0.977 0.974 0.978 0.984 0.978 | 0.974 | 0.928 I 0.891 1 0.978 1 0.981 I 0.980 1 0.979 0.983 1 0.978 1 0.981 1 0.985 1 0.977 | 0.971 | 0.980 I 0.921 1 0.978 1 0.974 1 0.980 1 0.977 ! 0.982 ! "-999" indicates concentration below analytical detection limit (ADL).------- TABLE C-3. SUMMARY OF CONCENTRATION AND PURITY FOR CANJ Sample Date I2-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 29-Aor-90 1 l-Mav-90 23-Mav-90 04-Jun-90 16-Jun-90 28-Jun-90 lO-Jul-90 Week Day M ID Number Lot 1166 | 46 St 1 178 46 Th T Sn F W M St Th T 1190D 1200 1215 1232 1242 1260 1270 1282 46 46 51 51 51 51 51 51 Formaldehyde Tubel (Ppb) 8.96 2.99 4.34 5.03 3.84 2.48 3.07 2.90 5.32 9.52 1288 55 | 8.87 22-Jul-90 Sn 1310 1 55 9 26 03-Aug-90 15-Aug-90 27-Aug-90 F W M 08-Sep-90 j St 20-Sep-90 02-0ct-90 14-0ct-90 26-Oct-90 07-Nov-90 19-Nov-90 Ol-Dec-90 Th T Sn F W M St 13-Dec-90 I Th 25-Dec-90 T 06-Jan-91 Sn 18-Jan-91 ) F 30-Jan-91 I W ll-Feb-91 M 23-Feb-91 I St 1319 55 1337 1361 1369 1384 1403 1422 1438 1463D 1472 1494 1505 1513D 55 55 55 55 55 51 51 56 49 49 49 60 1531 60 1548 1570D 60 60 1586D 60 1597 62 |_ 9.05 8.21 7.23 3.08 3.13 4.03 5.04 2.32 3.64 3.12 4.81 5.20 3.38 428 2.64 5.40 2.81 3.08 Tube 2 (ppb) Tubel Purity 8.16 0.997 3.83 0.987 4.34 0.997 4.84 0.991 3.64 0.989 2.24 3.09 2.82 0.996 0.993 0.992 5.26 0.999 9.44 0.994 Tube 2 Purity 0.995 0.980 0.997 0.997 0.991 0.969 0.987 0.972 0.997 0.961 8.82 0.990 0.996 8.97 1.000 0.999 10.57 0.971 0.998 8.38 6.91 0.999 | 0.998 0.999 3.23 0.999 3.35 4.03 5.05 2.38 3.61 3.18 4.82 4.95 3.21 1.000 1.000 1.000 0.999 1.000 0.999 1.000 1.000 0.997 0.997 1.000 0.999 0.999 1.000 0.999 1.000 1.000 1 1.000 1.000 1 1.000 4.43 | 1.000 | 0.999 2.40 [ 0.999 5.09 2.82 1.000 0.999 2.89 | 0.998 1.000 1.000 0.999 0.998 Acetaldchyde Tubel (PI*) Tube 2 (PP«>) Tubel Purity 4.39 4.79 0.995 1.86| 1.87 1.93 2.61 1.91 1.01 1.30 1.30 2.02 3.90 3.52 3.51 4 10 4.03 3.13 1.08 2.10 1.38 2.90 1.42 2.08 1.87 2.66 2.82 1.91 2.22 1.40 2.48 1.38 1.54 2.03 2.44 1.58 0.85 1.23 1.18 1.85 3.84 4.19 0.412 0.997 0.991 0.980 0.997 0.997 0.987 0.985 0.970 0.979 3.21 0.994 3.81 1 0.991 4.30 3.22 1.19 2.43 1.90 2.91 1.46 2.14 1.75 2.53 2.77 0.995 0.978 0.979 0.987 0.993 0.992 0.991 0.992 0.991 0.992 0.993 1.82 | 0.993 2.29 | 0.993 1.32 2.41 1.34 1.42 0.992 0.992 0.993 0.992 Tube 2 Purity Acetone Tubel (ppb) 0.995 4.41 0.995 Tube 2 (ppb) 3.96 2.63 2.09 0.991 2.37 0.994 0.904 0.887 2.37 1.41 1.52 0.988 1.77 0.989 1.06 0.996 | 1.68 0.999 3.75 0.996 2.90 2.11 2.38 1.56 1.28 2.25 1.19 1.58 4.19 3.01 0.994 2.49 | 2.63 0.945 4.23 6.38 0.921 4.39 4.48 0.998 2.78 3.17 0.995 0.991 0.992 0.993 0.992 0.993 0.992 0.992 0.993 1.94 3.52 2.40 1.38 1.79 2.11 1.22 1.71 1.97 0.994 I 1.33 0.993 | 1.77 0.992 | 1.30 0.993 0.993 2.40 1.04 0.992 | 1.37 2.08 2.90 2.41 1.42 1.79 1.96 1.16 1.84 1.83 1.20 Tubel Purity 0.933 0.394 0.541 0.981 0.969 0.967 0.654 0.570 0.630 0.980 0.958 Tube 2 Purity 0.945 0.988 0.864 0.692 0.973 0.855 0.976 0.971 0.873 0.953 0.980 0.981 | 0.983 0.920 0.984 0.972 0.603 0.850 0.982 0.974 0.980 0.978 0.955 0.983 0.978 0.981 1.73 | 0.807 1.24 2.39 1.05 1.29 0.976 0.967 0.964 0.973 0.957 0.939 0.957 0.974 0.973 0.979 0.968 0.980 0.982 0.979 0.981 0.981 0.982 0.992 0.979 0.979 0.966 0.981 "-999" indicates concentration below analytical detection limit (ADL).------- TABLE C-4. SUMMARY OF CONCENTRATION AND PURITY FOR H1TX Sample Date 12-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 1 l-May-90 23-Mav-90 04-Jun-90 16-Jun-90 22-Jul-90 | 03-Aug-90 j 15-AUR-90 ! 27-Aug-90 Week Day M St Th T F W M St Sn F W M ID Number 1170D Lot 46 1184 1 46 | 1187 | 1210 1230D 1245 1255 1267 1308 1323 46 46 51 51 51 51 55 55 1334 | 55 1357 55 08-Sep-90 | St | 1373D i 55 20-Sep-90 Th 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 19-Nov-90 Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-9! j 30-Jan-91 ' ll-Feb-91 23-Feb-91 T Sn F W M St Th T Sn F W | M St 1390 1413 1426 1435 1451 1474 1488 1502 1519 1539D 1544 55 55 51 51 51 49 49 49 60 60 60 1558 1 60 Formaldehyde Tube 1 (ppb) 0.36 1.17 | 1.08 1.91 0.64 2.11 2.01 1.61 1.02 1.13 1.95 Tube 2 (ppb) 0.94 1.65_[ 1.16 1.69 0.61 2.52 1.86 1.62 1.14 1.16 1.86 Tubel Purity Tube 2 Purity Acetaldehvde Tubel (Ppb) 0.921 I 0.912 0.40 0.997 i 0.930 1 0.83 | 0.997 I 0.925 1 0.941 0.998 0.990 0.972 0.999 0.994 1.000 0.996 0.996 0.925 0.978 0.992 0.978 0.998 0.996 -999 0.85 0.37 0.83 0.69 0.36 0.38 -999 0.995| 1.14 1.53 1.31 I 0.996 | 0.993 | 0.79 1.04 1.02 i 0.994 | 0.993 | -999 1.29 1.31 1.50 1.99 1.28 1.21 1.65 2.28 1.31 1.48 1.48 1.21 1 1.000 1.58 1.60 2.03 1.33 1.07 1.64 1.88 1.34 1.56 1.55 0.52 0.59 1.000 1.000 1.000 1.000 0.999 0.999 1.000 0.978 1.000 0.999 1.000 1574 1 60 | 2.48 | 2.61 I 1. 000 1598 62 | 1.38 1.40 1.000 0.999 0.68 0.999 1 0.94 0.994 | 1.21 1.000 1.000 1.000 1.000 1.000 1.000 1.000 1.000 1 1.03 0.77 0.89 0.69 0.62 I 0.86 j 0.45 | 0.40 Tube 2 (ppb) 0.45 0.44 -999 0.45 -999 1.18 0.89 0.55 0.38 0.38 1.28 0.80 -999 0.68 1.07 1.36 1.39 0.83 0.97 0.67 0.52 0.87 0.43 0.43 0.998 i 0.36 i 0.40 Tubel Purity Tube 2 Purity 0.927 ! 0.970 0.926 I 0.849 0.966 0.948 0.988 0.992 0.937 0.988 0.947 0.887 0.975 0.981 0.918 0.871 0.985 0.984 0.951 0.978 0.886 0.984 0.998 | 0.946 0.998 1 0.984 0.993 0.993 0.993 0.994 0.990 0.993 0.977 0.989 0.989 0.993 0.990 0.979 | 1.000 | 1.16 | 1.13 | 0.993 i 1.000 i 0.70 0.70 0.992 0.992 0.992 0.993 0.992 0.993 0.992 0.992 0.989 0.990 0.991 0.990 I 0.967 0.991 | 0.991 Acetone Tube 1 (PP*>) Tube 2 (ppb) -999 ) 0.62 0.71 1.07 0.62 0.81 0.94 0.53 0.38 0.43 1 -999 1 0.63 1.04 0.65 0.85 0.79 1.37 0.62 0.51 -999 -999 Tubel Purity 0.917 0.895 0.763 0.900 0.667 0.817 0.851 0.729 0.667 0.928 0.64 1 0.975 1 0.77 I 0.55 1 -999 -999 0.979 -999 | 0.667 -999 1.12) 1.36 0.79 0.72 0.70 0.45 -999 0.38 -999 -999 -999 -999 0.97 1 0.42 0.84 0.46 0.78 0.38 -999 -999 -999 -999 -999 0.39 0.68 0.44 0.667 0.979 0.924 0.791 0.788 0.955 0.667 0.973 0.667 0.667 0.667 0.667 0.790 0.817 Tube 2 Purity | 0.851 1 0.726 1 0.743 1 0.926 1 0.768 I 0.805 1 0.736 1 0.740 | 0.667 | 0.752 1 0.883 1 0.979 1 0.908 I 0.667 1 0.979 | 0.932 0.667 0.790 0.816 0.667 0.667 0.805 0.667 0.667 0.667 0.783 0.817 "-999" indicates concentration below analytical detection limit (ADL).------- TABLE C-5. SUMMARY OF CONCENTRATION AND PURITY FOR ORFL Sample Date lO-Jul-90 16-Jul-90 22-Jul-90 28-Jul-90 03-Aug-90 09-Aug-90 15-Aug-90 27-Aug-90 02-Sep-90 08-Sep-90 Week Day T M Sn St F Th W M Sn St 14-Sep-90 | F 20-Sep-90 | Th 26-Sep-90 1 W 08-0ct-90 14-Oct-90 20-Oct-90 26-Oct-90 Ol-Nov-90 07-Nov-90 13-Nov-90 Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-9l ll-Feb-91 23-Feb-91 M Sn St F Th W T St Th T Sn F 1 W M St ID Number 1290 1302 1307 1316 1320 1332 1350 1359 1363 1377 1383 1386 1397 1418 1424 1432 1446 1449D 1465 1466 1484 1508D 1522 1533 1554D 1567 1580 1596 Lot 51 55 55 55 55 55 55 55 55 55 55 55 55 55 51 55 51 55 56 49 49 49 60 60 60 60 60 62 Formaldehyde Form (PP»>) 3.41 2.35 3.49 2.17 3.28 3.37 Form (PP*>) 3.69J 2.68 3.58 3.47 3.02 3.66 3.32 | 3.35 4.38 2.84 4.53 3.92 4.57 2.72 4.55 4.05 Form Purity 0.993 Form Purity Acetaldehyde Acetald (PI*) 0.998 | -999 0.998 I 0.998 0.59 1.000 | 0.993 | 1.02 0.998 0.986 0.999 0.998 1.000 1.000 1.000 0.995 0.998 0.997 0.999 0.995 0.999 0.998 0.47 1.00 1.42 0.98 1.13 1.01 0.998 | 1.07 0.990 1 1.18 -999 0.42 0.893 0.982 3.36 1.87 32.97 1.93 3.22 2.35 3.45 4.26 2.10 7.02 6.29 1.83 3.51 1.83 34.11 2.10 3.19 2.34 3.28 4.41 2.14 6.99 6.46 1.79 3.50 3.45 3.46 1.000 1.000 1.000 1.000 0.999 1.000 1.000 1.000 1.000 0.999 1.000 0.997 0.999 1.000 1.000 1.000 0.999 1.000 1.000 1.000 0.999 0.998 1.000 1.000 -999 0.98 0.49 4.61 0.88 1.75 0.95 1.27 1.74 1.01 2.96 2.66 0.64 1.000 1.000 1.35 3.72 I 0.999 3.54 | 3.65 2.36 2.52 1.000 0.999 0.999 1.22 1 1.000 0.999 1.45 1.00 Acetald (PI*) -999 0.50 1.16 0.98 0.99 1.48 1.02 1.26 0.80 0.83 1.10 0.53 1.02 0.48 14.20 0.97 1.22 0.96 1.21 1.79 1.03 2.85 2.68 0.70 1.34 1.30 1.48 1.08 Acetald Purity 0.979 0.978 0.994 0.969 0.815 0.969 0.986 0.958 0.974 0.999 0.977 Acetald Purity 0.994 Acetone | AfftmiK (PI*) 0.37 0.972 | -999 0.943 0.997 0.965 0.989 0.932 0.996 0.992 0.983 -999 -999 -999 0.89 -999 0.45 -999 0.62 0.998 | 0.72 0.963 0.979 | -999 0.992 0.992 0.991 0.993 0.990 0.992 0.993 0.992 0.993 0.992 0.994 0.992 0.992 0.991 0.993 0.992 0.992 0.993 0.993 0.990 0.986 0.993 0.991 0.990 0.987 0.995 0.993 1.01 -999 -999 0.62 1.97 1.06 0.95 1.24 0.56 0.65 0.39 0.992 I 0.40 0.992 1.73 0.992 1 0.51 0.993 0.993 1.84 1.05 A/-*4rm> (P!*) Acetone Purity -999 0.987 0.69 0.57 -999 -999 0.65 -999 0.49 0.43 0.71 0.81 1.08 1.06 0.44 10.79 0.57 2.10 1.20 1.11 1.63 ' 0.42 1.80 0.49 0.46 2.15 0.70 2.09 1.21 0.907 0.934 0.896 0.619 0.862 0.916 0.856 0.900 0.592 0.971 0.883 0.978 0.969 0.000 0.975 0.981 0.969 0.966 0.962 0.980 0.801 0.796 0.943 0.972 0.979 0.974 0.968 Acetone* Purity j 0.930 0.942 | 0.913 | 0.788 | 0.813 1 0.988 0.588 0.947 0.885 1 0.929 1 0.960 i 0.884 1 0.947 1 0.983 | 0.984 0.964 0.967 0.975 0.971 0.969 0.965 0.963 0.915 0.894 0.976 0.980 0.974 0.971 "-999" indicates concentration below analytical detection limit.------- TABLE C-6. SUMMARY OF CONCENTRATION AND PURITY FOR PEFL Sample Date 10-Feb-90 22-Feb-90 12-Mar-90 24-Mar-90 OS-Apr-90 17-Apr-90 29-Apr-90 1 l-Mav-90 23-May-90 04-Jun-90 16-Jun-90 28-Jun-90 Week Day St Th M St Th T Sn F W M St ID Number 1158 Lot 46 1159 i 46 1 174 46 1186D I 46 1194 1206 1213 1225 1250 1257 1263 Th 1279 46 46 51 51 51 51 51 51 Formaldehyde Tubel (PP*>) 1.11 1.42 2.56 1.79 3.80 2.96 2.13 1.97 2.78 1.67 5.23 0.98 10-Jul-90 T 1298 51 3.41 16-Jul-90 M 22-Jul-90 Sn 28-Jul-90 03-Aup-90 09-Aug-90 15-Aug-90 21-Aug-90 27-Aug-90 02-Sep-90 08-Sep-90 14-Sep-90 20-Sep-90 1301 55 | 2.05 1313 St 1318 F Th W T M Sn St F Th 26-Sep-90 i W 02-Oct-90 1 T 08-Oct-90 M 14-Oct-90 20-Oct-90 Sn | St 26-Oct-90 I F 1327 1330 1339 1349 1353 1364 1368 1381 1388 55 1 1.46 55 55 55 55 55 55 55 55 55 55 1402 55 4.57 3.56 4.17 4.38 2.66 1.64 2.65 3.43 1.68 2.52 3.68 1406 55 I 1.68 1415 55 1423 1431 1444 Ol-Nov-90 Th | 1448 07-Nov-90 W 51 55 51 55 1458 56 14-Nov-90 i W 1467 Ol-Dec-90 St 13-Dec-90 I Th 25-Dec-90 1 T 06-Jan-91 Sn 18-Jan-91 1 F 30-Jan-91 1 W 12-Feb-91 | T 23-Feb-91 1 St 1495 1500 1517 49 49 60 60 1527 | 60 1545D | 60 1564 1582 60 60 I 1601D I 62 1.66 15.15 2.36 1.62 Tube 2 (Ppb) Tubel Purity 0.71 0.792 Tube 2 Puritv 0.939 1.34 0.978 0.985 2.47 0.965 0.998 1.58 0.998 3.92 0.994 3.06 0.771 1.96 2.38 2.94 2.06 5.08 0.83 0.987 0.983 0.998 0.982 0.977 0.996 0.996 0.943 0.963 0.957 0.995 0.994 1 0.988 Acetaideayde Tubel 0.67 -999 1.15 1.41 1.48 1.10 0.61 0.63 0.78 0.58 1.21 0.994 0.995 | -999 3.51 0.927 0.997 1.91 0.992 0.997 1.67 5.48 3.66 4.13 0.997 0.999 0.992 0.999 0.996 0.998 0.990 4.31 0.999 2.59 1.77 2.50 3.76 1.93 2.71 3.77 0.994 0.991 0.997 0.995 0.996 1.000 0.972 0.994 0.996 0.986 0.997 0.998 0.980 0.995 1.000 I 1.000 1.66 1.000 0.999 1.76 -999 2.38 1.000 1.000 0.999 1.000 0.000 1.000 1.72 0.999 0.999 2.21 2.30 1.000 2.04 2.14 1.57 1.44 0.87 1.09 1.24 2.17 1.000 2.30 1 0.999 1.000 0.43 0.51 -999 0.96 0.45 1.01 1.08 0.81 0.40 0.43 0.93 0.38 0.71 1.44 0.47 0.48 2.73 0.73 0.53 1.16 1.000 I 0.89 1.000 1.56 1.000 1.000 1.54 1.000 0.98 1.10 1.21 1.000 1.000 0.996 0.59 0.88 ! 0.999 2.87 0.88 3.04 0.999 1.000 1.000 1.000 0.999 0.984 0.999 1.23 0.92 0.84 0.64 0.47 0.70 0.39 1.78 0.88 0.998 1 0.999 I 0.69 Tube 2 (PP*>) 0.53 -999 0.96 1.72 1.55 1.19 0.88 0.52 0.76 0.58 1.02 Tubel Purity 0.954 0.962 0.972 0.970 0.988 0.599 0.985 0.995 0.982 0.973 0.992 0.76 0.981 0.39 0.796 0.44 0.985 -999 0.994 1.58 | 0.901 0.54 1.14 1.27 0.66 0.51 -999 0.85 -999 0.74 1.48 0.995 0.986 0.991 0.879 0.964 0.991 0.974 0.946 0.970 0.992 Tube 2 Purity Acetone i Tubel (ppfe) 0.985 I 1.22 Tube 2 (PP*») 1.03 Tubel Puritv 0.929 Tube 2 I Purity! 0.881 1 0.947 i 1.81 1.68 1 0.907 ( 0.875 1 0.682| 1.1.3 2.36 0.983 1 1.89 0.994 0.986 0.978 | 0.885 0.890 0.895 0.884 0.997 2.93 1.49 0.62 0.96 1.43 0.37 1.56 0.63 1.89 3.07 1.53 0.70 1.21 1.31 0.42 0.80 0.986 0.936 0.607 0.748 1 0.931 1 0.996 1 0.428 I 0.972 1 0.469 1.000 0.952 0.802 0.803 -999 0.946 0.988 | -999 -999 0.952 0.902 1 1 . 1 1 0.992 -999 0.954 0.990 0.975 0.997 0.986 0.946 0.980 0.990 0.960 2. (50 -999 2.69 1.76 0.41 0.44 0.46 0.72 -999 0.987 1 .27 0.993 3.33 0.940 1 0.875 I 0.824 | 0.817 ! 0.667 0.930 0.927 0.95 0.946 | 0.901 -999 | 0.611 2.97 -999 2.34 1.34 -999 0.41 0.63 0.89 -999 1.64 3.45 0.78! 0.985 0.969 0.875 0.931 0.979 0.880 0.896 0.868 0.911 0.790 0.984 0.982 0.963 0.953 0.832 0.570 | 0.912 I 0.853 | 0.749 1 0.786 1 0.977 1 0.982 1 0.51 0.992 0.991 -999 | -999 0.883 | 0.878 I 0.53 -999 0.78 0.64 1.12 0.95 1.34 0.84 0.86 0.69 0.50 0.75 0.39 1.83 0.68 0.993 0.990 0.991 0.992 0.990 0.990 0.993 0.982 0.991 0.992 0.992 0.990 0.000 0.47 10.56 0.986 | 2.30 0.992 0.991 0.990 0.990 0.983 0.989 0.991 0.991 0.991 0.991 0.976 0.993 0.991 0.964 0.994 1.44 2.57 1.80 1.93 0.47 2.51 0.82 0.51 1.33 -999 1.95 0.51 0.957 | 0.966 1 -999 2.31 1.48 2.71 1.90 1.82 0.45 2.59 0.93 0.47 1.34 -999 0.982 0.975 0.974 0.978 0.980 0.977 0.982 0.980 0.975 0.965 0.974 0.909 2.05 0.977 0.992 1.30 1.31 0.000 I 0.967 I 0.982 1 0.980 1 0.981 j 1 0.976 1 0.977 j 0.979 | 0.970 I 0.956 1 0.974 | 0.906 1 0.977 1 0.972 j 0.976 "-999" indicates concentration below analytical detection limit (ADL).------- TABLE C-7. SUMMARY OF CONCENTRATION AND PURITY FOR PNTX Sample Date 12-Mar-90 Week Day M 24-Mar-90 | St 05-Apr-90 !7-Apr-90 29-Apr-90 ll-Mav-90 23-May-90 04-Jun-90 l6-Jun-90 28-Jun-90 10-Jul-90 22-Jul-90 03-Aug-90 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 30-Nov-90 Ol-Dec-90 13-Dcc-90 25-Dec-90 06-Jan-9 1 18-Jan-91 30-Jan-91 lt-Feb-91 23-Feb-91 Th T Sn F W M St Th T Sn F W M St Th T Sn F W F St Th T Sn F W M St ID Number Lot 1130 46 1183D 1192 1201 1212D 1224 1240 1256 1271 1281 46 46 46 51 51 51 51 51 51 1289 55 1305 1328 55 55 1335 55 1351 ^ 1371 1392 1414 1420 1437 1454 1469 1482 1499 1521 1532 1543 1559 1576 1592 55 55 55 55 51 51 56 49 49 49 60 60 60 60 60 62 Formaldehyde Tube I (PF*) 2.64 Tube 2 (PP»») 6.23 2.69 1 10.05 3.33 4.42 2.17 -999 4.67 3.18 3.08 5.52 3.23 2.19 2.87 5.63 8.80 4.34 3.77 2.84 5.02 5.68 4.09 4.87 5.07 2.58 4.70 3.80 7.32 2.21 7.13 4.43 3.63 9.19 6.00 -999 10.30 3.27 5.46 9.17 3.20 2.66 Tubel Purity 0.980 0.991 0.992 0.998 0.991 0.910 0.995 0.997 0.993 0.997 0.994 Tubel Purity 0.965 0.999 0.998 0.997 1.000 0.933 0.992 0.990 0.998 0.994 0.996 Acetaldcfayde Tubel (ppb) 3.77 3.90 1.55 2.89 0.68 -999 2.02 1.44 1.98 4.67 1.92 0.998 0.998 0.55 6.45 | 0.999 1.000 10.09 8.12 3.90 3.24 2.82 5.82 5.65 5.13 5.52 5.57 4.14 4.74 4.19 7.14 2.66 7.42 4.85 0.999 0.998 0.999 1.000 1.000 1.000 1.000 1.000 1.000 1.000 1.000 0.999 1.000 0.999 1.000 1.000 0.992 0.998 0.999 1.000 1.000 0.999 1.000 1.000 0.999 1.000 1.000 0.999 0.999 0.999 0.999 0.999 0.999 1.000 1.52 3.10 4.16 2.07 2.54 1.14 3.07 2.18 1.85 3.53 3.59 1.11 2.12 2.47 1.81 0.80 3.39 1.42 Tube 2 (PP»>) Tubel Purity Tube 2 Purity Acetone Tubel (PI*) 4.69 0.988 0.994 1 0.99 4.80 0.889 2.12 3.08 1.00 -999 1.83 1.36 2.26 5.77 2.05 0.997 0.994 0.918 0.978 0.994 0.982 0.987 0.995 0.980 I 1.94 0.997 0.960 0.985 0.981 0.992 0.997 0.994 0.988 0.995 0.996 1.42 1.55 -999 -999 1.46 0.45 0.36 j_ 1.76 -999 Tube 2 (PP«») 1.54 2.57 1.73 1.35 -999 -999 1.32 0.37 0.59 1.79 -999 0.67 0.994 0.986 -999 -999 1.90 3.58 3.60 1.86 2.49 1.14 3.45 2.14 2.21 4.22 3.88 1.22 2.11 2.49 1.73 0.78 3.72 1.58 0.997 0.999 -999 0.995 0.990 0.993 0.992 0.993 0.992 0.992 0.991 0.993 0.993 0.991 0.993 0.993 0.991 0.991 0.992 0.993 0.950 0.985 0.998 0.992 0.992 0.993 0.990 0.991 0.993 0.992 0.992 0.993 0.993 1.46 1.90 0.50 0.59 0.60 0.96 1.85 -999 -999 0.49 -999 0.81 0.46 0.992 0.87 0.992 0.992 0.992 1.04 2.80 1.54 0.41 1.52 1.63 0.48 0.58 0.58 1.13 2.00 1.51 0.44 -999 -999 0.84 0.44 0.89 0.84 2.92 1.49 Tubel Purity 0.484 0.876 0.931 0.575 0.871 0.797 0.816 0.840 0.988 0.997 0.916 0.795 0.893 0.797 0.958 0.838 0.960 0.953 0.987 0.987 0.667 0.674 0.907 0.667 0.817 0.763 0.815 0.787 0.980 0.794 Tube 2 Purity 0.958 1 0.982 I 0.532 1 0.911 | 0.912 | 0.878 1 0.973 0.929 0.929 0.987 | 0.898 1 0.925 1 0.996 1 0.812 | 0.986 1 0.922 0.871 0.951 0.786 0.988 0.989 0.884 0.807 0.917 0.818 0.894 0.818 0.922 0.977 0.793 "-999" Indicates concentration below analytical detection limit (ADL).------- TABLE C-8. SUMMARY OF CONCENTRATION AND PURITY FOR SAIL Sample Date 12-Mar-90 1 24-Mar-90 1 05-Apr-90 16-Apr-90 1 l-May-90 I 23-May-90 1 04-Jun-90 16-Jun-90 28-Jun-90 10-Jul-90 24-Jul-90 Week Day M St Th M F W M St Th T T ! 03-AU8-90 1 F !4-Aug-90 | T j 27-AUB-90 08-Sep-90 25-Seo-90 02-0ct-90 14-Oct-90 26-Oct-90 07-Nov-90 19-Nov-90 Ol-Dec-90 13-Dec-90 27-Dec-90 06-Jan-91 18-Jan-91 M St T T Sn F W M St Th Th 1 Sa 1 F 30-Jan-91 I W 12-Feb-91 23-Feb-91 1 T 1 St ID Number 1165 | 1177 1195 1208 1226 I 1246 1262 1269 1280 1294 1315 Lot 46 46 46 46 51 51 51 51 Formaldehyde Tubel (Ppb) 1.09 1.42 1.92 1.52 1.00 1.94 3.26 4.79 51 | 1.82 55 55 7.23 2.50 1329 I 55 1 3.44 L 1344 i 55 1354 1372 1401 1404 1419 1441 146 ID 1471 149 ID 1501 1523 55 55 55 55 51 51 56 49 49 49 60 { 1535 1 60 1552D I 60 1565 1581 1604D 60 60 62 2.74 6.14 3.10 3.45 4.40 3.07 2.14 1.87 2.75 1.11 1.54 1.75 1.74 1.87 1.83 1.73 2.01 Tube 2 (PP»>) 1.23 | Tubel Purity Tube 2 Purity 0.983 1 0.956 | 1.62 1 0.984 I 2.40 1.25 0.93 j 0.974 1 0.990 0.970 1.99 | 0.991 2.83 1.39 1.94 7.22 2.45 0.988 0.998 Acetaldefayde Tubel (ppb) 0.50 | 0.999 I 1.30| 0.983 0.988 0.993 0.976 0.983 0.996 0.965 I 0.967 0.995 0.990 0.996 0.994 1.03 0.45 0.50 1.18 1.63 j 1.53 | -999 1.95 0.82 0.49 1 0.999 0.995 | 0.77 2.88 I 0.992 0.998 ! 0.79 6.15 3.21 0.999 1.000 0.998 0.999 3.44 1 1.000 4.67 2.60 2.02 1.88 3.61 1.14 1.42 1.90 1.68 1.89 1.69 1.71 1.88 1.000 0.999 1.000 1.000 1.000 0.999 | 1.000 1.000 1.000 1.000 0.998 0.999 0.999 0.999 0.997 0.999 1. 000 0.999 1 1.000 1.000 | 0.999 0.999 1 1.000 1.000 0.999 1.000 1.000 1.18 1.22 1.04 1.47 1.10 1.40 1.03 1.55 0.71 0.96 1.26 Tube 2 (ppb) 0.53 | Tubel Purity 0.764 1 1.36 j 0.969 1 1.02 | 0.62J 0.70 | 0.93 1.68 -999 -999 1.83 0.79 0.971 j 0.985 0.990 0.992 0.995 0.999 0.972 0.987 Tube 2 Purity Acetone ] Tubel (Ppb) Tube 2 (ppb) Tubel Purity 0.987 1 0.44 | 0.63 1 0.909 0.993 | 1.79 | 1.26 | 0.961 0.965 | 1.51 0.927 j 1.28 | 0.994 0.987 0.88 1.36 0.944 1 0.87 0.923 1 0.880 0.74 0.59 0.976 I 0.94 0.994 1 0.983 1 1.85 0.52 1 0.961 | 0.980 1 0.94 0.74 1.05 0.97 1.10 1.59 0.98 1.15 1.06 2.03 1.03 0.99 1.36 1.25 | 1.22 0.92 1.02 0.86 0.95 0.90 1.02 0.89 0.95 0.965 0.986 0.993 0.993 0.992 0.991 0.992 0.989 0.991 0.989 0.989 0.993 0.993 | 0.85 0.983 0.983 0.992 0.992 0.990 0.991 0.990 0.992 0.991 0.976 0.993 0.990 I 0.990 | 0.992 ! 0.992 0.990 0.988 | 0.991 0.991 0.990 0.988 0.47 0.85 2.84 3.10 1.91 1.17 1.05 1.33 0.76 0.68 0.88 1.52 | 1.34 I 0.583 0.855 1.03 | 0.971 1.35 | 0.89 -999 0.51 1.29 1.39 1.17 1.08 0.64 0.86 2.98 3.20 1.90 1.20 1.02 1.62 0.73 0.74 0.97 | 0.93 0.91 | 1.13 1.05 0.85 1.10 0.989 0.911 0.976 0.745 0.919 0.793 0.983 0.907 0.863 0.998 0.977 0.983 0.977 0.964 0.965 0.977 0.969 0.980 0.975 Tube 21 Puritv 1 0.988 1 0.876 1 0.521 I 0.796 1 0.585 1 0.953 I 0.816 1 0.727 1 0.807 0.993 0.898 0.778 0.990 0.949 0.626 0.962 0.983 1 0.982 | 0.977 | 0.953 1 0.977 J 0.969 | 0.968 I 0.978 1 0.983 0.983 1 | 1.08 | 0.978 1.09 0.80 1.10 0.971 0.980 0.969 0.975 1 0.974 1 0.968 1 0.964 1 "-999" indicates concentration below analytical detection limit (ADL).------- TABLE C-9. SUMMARY OF CONCENTRATION AND PURITY FOR TLOH Sample Date 05-Apr-90 16-Apr-90 29-Apr-90 1 l-Mav-90 23-Mav-90 04-Jun-90 16-Jun-90 28-Jun-90 10-Jul-90 22-Jul-90 03-Aug-90 15-Aue-90 27-Auj»-90 08-Sep-90 20-Sep-90 02-Oct-90 l4-Oct-90 26-Oct-90 07-Nov-90 19-Nov-90 Ol-Dec-90 13-Dec-90 Week Day Th M Sn F W M St Th T Sn F W M St Th T Sn F W M St Th ID Number 1193 1205D 1214 1223 1243 1253 1264 1278 1293 1306 Lot 46 46 51 51 51 51 51 51 55 55 1326 | 55 1345 1355 1367 1387 1410 1425 1440 1455 1478D 1486 1507 Formaldehyde Tube 1 (ppb) 1.75 1.22 1.57 1.21 1.87 0.75 4.21 2.05 3.45 1.52 3.92 55 I 4.91 55 55 55 55 51 51 56 49 49 49 5.52 2.58 1.19 2.64 1.99 2.06 1.65 3.48 1.94 2.10 Tube 2 (ppb) 2.01 1.63 1.48 1.23 1.58 0.83 2.12 1.98 3.46 1.60 4.46 4 89 5.33 2.14 1.51 2.70 2.13 1.72 1.54 3.41 2.16 1.97 Tube 1 Purity 0.921 0.910 0.972 0.987 0.992 0.916 0.994 0.955 0.986 0.995 0.997 0.999 1.000 0.998 0.998 1.000 1.000 0.997 1.000 1.000 1.000 1.000 Tube 2 Purity 0.992 0.971 0.984 0.958 0.981 0.904 0.981 0.975 0.952 0.968 0.999 0.999 1.000 0.987 0.992 1.000 1.000 1.000 1.000 0.999 0.998 1.000 Acetaldehyde Tube 1 (ppb) 0.50 0.87 0.87 -999 1.04 -999 1.69 -999 1.04 -999 2.51 1.42 1.83 1.59 -999 1.39 -999 0.68 0.82 2.54 1.01 0.59 Tube 2 (ppb) Tubel Purity 0.90 I 0.925 1.14 1 0.965 0.62 1 0.937 -999 | 0.961 1.06 -999 0.76 -999 0.986 0.940 0.995 0.983 0.48 1 0.981 -999 0.987 2.79 1 0.976 1.35 1.31 0.73 0.984 Tube 2 Purity 0.940 0.933 0.957 0.907 0.985 0.958 0.964 0.974 0.990 0.816 0.990 0.960 0.980 | 0.984 0.958 0.55 | 0.976 1.33 -999 -999 0.80 2.17 1.12 -999 0.992 0.989 0.992 0.989 0.978 0.981 0.992 0.953 0.944 0.992 0.990 0.991 0.988 0.975 0.988 0.993 Acetone Tube 1 (ppb) 1.43 1.221 1.55 0.89 2.26 0.58 1.39 0.71 2.25 1.23 2.92 3.46 0.80 1.43 1.45 2.16 2.14 1.33 1.20 1.52 1.23 0.95 Tube 2 (ppb) 1.47 1.19 1.30 0.76 1.82 0.52 0.68 0.67 1.90 1.45 3.39 3.99 Tubel Purity 0.938 0.940 0.952 0.959 0.863 0.954 0.932 0.935 0.890 0.974 0.987 Tube 2 Purity 0.977 1 0.879 1 0.901 I 0.645 0.970 0.953 0.995 0.923 0.972 0.863 0.991 0.874 1 0.975 0.72 t 0.965 1.35 1.58 2.27 2.13 1.37 1.11 1.55 1.35 1.04 0.931 0.945 0.983 0.969 0.967 0.978 0.978 0.943 0.978 0.979 0.536 0.998 0.981 0.980 0.973 0.979 0.973 0.972 0.981 "-999" indicates concentration below analytical detection limit (ADL).------- TABLE C-10. SUMMARY OF CONCENTRATION AND PURITY FOR W1DC Sample Date 12-Mar-90 24-Mar-90 05-Apr-90 17-Apr-90 29-Apr-90 1 l-Mav-90 23-May-90 04-Jun-90 16-Jun-90 28-Jun-90 10-Jul-90 22-Jul-90 03-Aug-90 Week Day ID Number M 1171 St 1 179 Th T Sn F W M St 1188 1203D 1220 1233 1249 1258 1265 Th 1284 T Sn F 15-Aug-90 W 27-Aug-90 M 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 19-Nov-90 Ol-Dec-90 St Th T Sn F W M St 13-Dec-90 | Th 25-Dec-90 i T 06-Jan-91 ! Sn 18-Jan-91 F 30-Jan-91 | W ll-Feb-91 | M 23-Fcb-91 St 1295 1309 1322 Lot 46 Formaldehyde Tube 1 (PP*>) 4.74 46 3.05 46 46 51 51 51 51 51 51 55 4.75 3.70 3.35 2.56 3.29 2.43 9.23 10.19 8.85 55 1 7.98 55 I 8.25 1340 55 1360 1379 1385 1411 1430 1442 1457 1480D 1485 55 55 55 55 51 51 56 49 49 1503 I 49 8.30 6.41 3.76 3.74 4.24 3.89 2.62 3.59 4.44 7.47 4.33 Tube 2 (ppb) 2.95 Tubel Puritv Tube 2 Purity 0.998 | 0.990 1.62 0.998 1 0.954 2.74 3.54 3.86 1.23 0.998 0.997 0.994 0.948 0.998 I 0.996 0.990 | 0.991 2.38 0.998 i 0.995 1.78 0.977 | 0.987 9.75 0.977 9.57 0.997 0.998 0.985 Acctaldefayde Tubel (ppb) 1.78 2.09 1.78 0.82 1.40 0.90 1.14 0.75 3.30 2.84 9.91 0.993 0.997 2.41 8.21 0.999 l.OOOl 1.97 [ 8.47 | 0.980 0.951 2.96 8.91 0.999 0.990 8.68 | 0.980 4.01 3.64 4.02 3.80 2.81 3.81 4.36 7.48 4.52 0.998 0.999 1.000 0.999 1.000 1.000 1.000 1.000 1.000 0.999 0.990 1.000 0.999 1.000 1.000 0.999 1.000 1.000 1.000 2.85 2.15 1.10 1.41 1.35 1.40 1.17 1.55 1.61 2.62 1.95 Tube 2 (PP»>) 0.96 1.37 1.29 0.51 1.35 0.47 0.73 0.56 3.84 2.69 2.38 1.69 3.12 2.54 2.34 0.99 1.01 1.33 1.29 1.28 1.62 1.66 2.62 1.92 1520 60 3.84 4.07 0.999 1.000 1.72 1.79 1528 60 3.71 1550 1566 1588D 1595 60 60 60 62 2.11 5.37 2.98 3.74. 3.71 1.000 0.999 | 2.04 2.07 2.10 0.999 5.56 1.000 3.16 0.999 . 3.90 l.OOOJ 0.99 0.999 1.000 1.000 0.999 2.08 1.18 1.50 1.05 2.06 1.11 1.54 Tubel Purity Tube 2 Purity Acetone j Tubel (ppb) 0.993 0.995 1 3. 09 0.929 0.992 1.83 0.923 0.991 I 1.90 0.983 0.997 0.973 0.993 0.963 0.995 0.997 0.996 0.968 0.997 0.974 0.982 0.983 0.988 0.981 0.987 2.13 1.48 1.29 1.22 1.19 2.4(5 2.30 0.972 1 1.67 Tube 2 (ppb) 2.69 1.15 1.16 2.38 1.70 0.73 1.02 0.77 3.40 3.05 Tubel Purity 0.991 0.500 0.990 0.989 0.761 0.635 0.963 0.977 0.988 0.965 2.28 1 0.864 0.991 1.77 1.95 0.951 0.904 2.55 4.63 0.987 0.960 0.978 0.991 0.993 0.992 0.992 0.993 0.992 0.993 0.993 0.862 2.67 3.12 0.986 2.31 0.989 0.871 0.993 0.993 0.993 0.992 1.15 2.22 1.99 1.04 1.25 1.50 0.993 1.12 0.993 1.75 0.992 2.75 1.43 2.37 2.01 1.19 1.32 1.70 1.38 0.932 0.939 0.991 0.791 0.693 0.961 0.978 0.970 0.974 0.977 0.985 2.02 0.984 0.91 1.79 0.965 Tube 2 | Purity | 0.662 1 0.981 | 0.998 | 0.626 1 0.949 1 0.925 I 0.967 1 0.952 1 0.832 I 0.954 1 0.995 0.963 1 0.959 1 0.859 1 0.945 0.975 1 0.875 I 0.977 0.973 0.980 0.977 0.968 0.985 0.977 0.992 0.993 1.12 1. 00 1 0.975 0.978 0.993 0.994 1.56 1.79 0.963 0.992 0.993 0.77 ) 0.85 i 0.971 0.992 0.992 1.64 0.992 0.992 0.74 1.85 0.982 0.85 0.970 0.992 0.994 1.16 1.13 0.972 0.975 0.966 1 0.975 1 0.972 1 0.971 "-999" indicates concentration below analytical detection.------- TABLE C-ll. SUMMARY OF CONCENTRATION AND PURITY FOR W1KS Sample Date 13-Mar-90 Week Day T 25-Mar-90 I Sn 05-Apr-90 17-Apr-90 29-Apr-90 1 l-Mav-90 23-Mav-90 04-Jun-90 16-Jun-90 28-Jun-90 10-Jul-90 Th T Sn F W M St Th T 22-Jul-90 [ Sn 03-Aug-90 I F 15-Aug-90 27-Aug-90 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 19-Nov-90 Ol-Dec-90 13-Dec-90 25-Dec-90 06-Jan-91 18-Jan-91 3 ------- TABLE C-12. SUMMARY OF CONCENTRATION AND PURITY FOR W2DC Sample Date 12-Mar-90 | 24-Mar-90 | 05-Apr-90 | 17-Apr-90 29-Apr-90 1 l-May-90 j 23-May-90 04-Jun-90 16-Jun-90 28-Jun-90 lO-Jul-90 Week Day M St Th | T Sn F W M St ID Number Lot 1172 I 46 1181 | 1191 1199 1217D j 1234 1247 1259 46 46 46 51 51 51 51 1266 | 51 Th | 1283 T 22-Jul-90 | Sn | OS-Aue-90 | F l5-Aup-90 | W 27-Aup-90 j M 08-Sep-90 20-Sep-90 02-Oct-90 14-Oct-90 26-Oct-90 07-Nov-90 19-Nov-90 Ol-Dec-90 13-Dec-90 I 25-Dec-90 06-Jan-91 18-Jan-91 30-Jan-91 ll-Feb-91 23-Feb-91 St Th T Sn F W M St Th T | Sn F W M St 51 Formaldehyde | Acetaldehyde 1 Tubel (PI*) 13.52 1 7.01 5.21 7.71 4.32 4.16 5.65 3.66 10.53 13.20 Tubel (PI*) Tubel Purity Tube 2 Purity Tubel (PI*) Tube 2 (PI*) 6.55 | 1.000 I 0.999 j 6.54 3.23 3.42 1 0.990 I 0.998 | 3.55 1 1.44 7.04 i 0.996 I 0.990 | 2.07 4.85 1 0.995 4.55 2.74 3.87 0.993 | 0.983 0.996 2.24 | 0.978 10.19 13.43 0.974 0.993 0.987 0.988 0.991 0.996 0.962 0.997 0.994 1292 55 I 11.94 i 10.33 1 0.936 i 0.993 1312 1 55 I 9.02 1325 1 55 1 11.66 1336 55 1356 1 55 1378 | 55 1389 1408 1429 1443 1456 1473 1489D 1506 55 55 51 51 56 49 49 49 1518 | 60 1529D | 60 1551 I 60 1568D 1583 60 60 1599D | 62 9.77 8.14 5.53 6.14 7.44 5.36 7.36 8.69 10.29 9.33 9.08 3.32 1.71 1.36 1.56 1.64 3.96 3.93 3.84 8.21 I 1.000 1 1.000 I 2.36 12.89 I 0.997 I 1.000 | 3.99 11.77 | 0.999 9.39 I 1.000 5.58 6.33 7.73 6.04 8.35 9.28 10.57 9.47 10.67 0.997 1.000 1.000 0.999 0.999 1.000 1.000 1.000 0.999 1.000 0.998 1.000 1.000 0.999 1.000 1.000 1.000 0.957 0.998 | 0.999 j 9.48 i 9.78 I 0.999 | 6.07 | 6.38 | 1.000 1 9.27 i 9.46 | 0.999 9.99 4.46 | 7.49 10.18 4.82 j 1.000 I 0.999 7.57 | 1.000 3.23 2.71 1.71 2.40 1.96 2.33 1.55 1.96 2.88 3.15 2.37 | 0.999 ! 1.81 | 0.999 | 2.40 0.999 1.000 0.999 0.999 1.71 2.74 1.47 1.45 2.50 1.45 1.86 0.71 1.20 1.11 4.96 3.70 Tubel Purfcy 0.994 | Tube 2 Purity Acetone ) Tubel (PI*) 0.977 I 6.86 Tube 2 (ppb) 3.61 j 0.989 | 0.975 I 2.75 | 0.92 0.985 ( 0.952 0.969 0.994 0.999 0.969 0.987 0.996 3.35 j 0.878 2.23 4.01 3.23 2.68 1.80 2.51 2.10 2.90 1.50 2.03 2.64 3.04 2.62 1.78 | 2.72 1.67 2.90 1.52 1.43 0.995 0.990 0.951 0.987 0.980 0.992 0.992 0.992 0.985 0.993 0.992 0.993 0.996 0.990 0.970 0.974 0.974 0.986 0.996 0.987 0.999 0.987 0.993 2.46 3.77 1.75 1.70 1.63 0.00 3.61 3.95 2.5* 1.77 2.02 2.67 0.91 1.53 0.91 3.94 5.06 2.00 Tubel Purity 0.900 0.941 | 0.595 0.650 0.998 0.935 0.816 0.911 0.933 0.908 0.829 1.000 1 1.97 | 2.16 I 0.995 0.990 | 4.26 0.997 | 3.68 0.995 0.985 0.992 0.993 0.993 2.58 1.83 2.78 2.67 | 1.22 0.992 1 1.22 0.984 0.991 0.993 ( 3.22 1.78 | 2.60 0.997 1 1.86 0.987 1 0.91 | 0.992 | 0.990 | 1.71 0.989 0.992 0.990 0.990 0.980| 1.17 0.993 0.993 0.978 ) 3.45 I 1.00 0.90 5.72 2.87 2.63 1.89 3.02 2.77 1.50 1.37 3.53 2.17 2.57 2.27 1.10 Tube 2 j Purity 0.994 1 0.566 1 0.908 1 0.995 1 0.493 | 0.903 1 0.798 1 0.945 I 0.915 1 0.884 1 0.971 I 0961 I 0.978 | 0.999 1 0.595 0.988 0.704 0.980 0.970 0.981 0.974 0.979 0.981 0.985 0.969 0.689 1 0.620 ! 0.982 1 0.982 I 0.970 1 0.980 | 0.979 i 0.982 I 0.967 1 0.984 | 0.919 1 0.817 0.789 1 1.71 | 0.973 1.42 4.60 1.15 1 0.94 0.667 0.982 0.973 0.902 0.667 0.667 0.972 0.978 0.667 "-999" indicates concentration below analytical detection limit (ADD.------- TECHNICAL REPORT DATA (Please read Instructions on the reverse before completing) 1. REPORT NO. EPA-450/4-91-001 3. RECIPIENT'S ACCESSION NO. 4. TITLE AND SUBTITLE 5. REPORT DATE 1989 Urban Air Toxics Monitoring Program Carbonyl Results July 1991 6. PERFORMING ORGANIZATION CODE 7. AUTHOR(S) 8. PERFORMING ORGANIZATION REPORT NO. Radian Corporation Research Triangle Park, N.C. 27709 9. PERFORMING ORGANIZATION NAME AND ADDRESS U.S. Environmental Protection Agency Research Triangle Park, N.C. 27711 10. PROGRAM ELEMENT NO. 11. CONTRACT/GRANT NO. 68-08-0014 12. SPONSORING AGENCY NAME AND ADDRESS 13. TYPE OF REPORT AND PERIOD COVERED 14. SPONSORING AGENCY CODE 15. SUPPLEMENTARY NOTES 16. ABSTRACT From Mar^h1990 through February 1991 samples of ambient air were collected at 12 sites in the eastern part of the U.S. Every 12 days, air was integrated over 24-hour periods into passivated stainless steel canisters. Simultaneously, air was drawn through cartridges containing dinitrophenylhydrazine to collect carbonyl compounds. The samples were analyzed at a central laboratory for a total of 37 halogenated and aromatic hydrocarbons, formaldehyde, acetaldehyde, and other oxygenated species. The hydrocarbon species were analyzed by gas chromatography/multiple detectors and gas chromatography/mass spectrometry, while the carbonyl species were analyzed by liquid chromatography. An extensive quality assurance program was carried on to secure high quality data. Complete data for all the carbonyl samples are presented in this report. 17. KEY WORDS AND DOCUMENT ANALYSIS DESCRIPTORS b.lDENTIFIERS/OPEN ENDED TERMS C. COSATI Field/Group UATMP-9Q Toxic Hydrocarbons Toxic Species Carbonyl Compounds 18. DISTRIBUTION STATEMENT Unlimited 19. SECURITY CLASS (This Report) Unclassified 21. NO. OF PAGES 133 20. SECURITY CLASS (This page) Unclassified 22. PRICE EPA Form 2220-1 (Rev. 4-77) PREVIOUS EDITION is OBSOLETE-------
xvEPA United States Environmental Protection Agency Office of Air Quality Planning and Standards Research Triangle Park NC 27711 EPA-450/4-91-025 July 1991 Air 1990 URBAN AIR TOXICS MONITORING PROGRAM CARBONYL RESULTS ------- EPA-450/4-91-025 1990 URBAN AIR TOXICS MONITORING PROGRAM CARBONYL RESULTS By Radian Corporation Research Triangle Park, NC 27709 EPA Contract No. 68D80014 EPA Project Officer: Neil J. Berg, Jr. Office Of Air Quality Planning And Standards Office Of Air And Radiation U. S. Environmental Protection Agency Research Triangle Park, NC 27711 July 1991 ------- This report has been reviewed by the Office Of Air Quality Planning And Standards, U. S. Environmental Protection Agency, and has been approved for publication. Any mention of trade names or commercial products is not intended to constitute endorsement or recommendation for use. EPA-450/4-91-025 ------- TABLE OF CONTENTS Page LIST OF FIGURES v LIST OF TABLES vii SYMBOLS AND ABBREVIATIONS viii 1.0 SUMMARY AND CONCLUSIONS 1-1 2.0 INTRODUCTION 2-1 3.0 UATMP FOR 1990 3-1 4.0 SAMPLING, ANALYSIS, AND QUALITY ASSURANCE PROCEDURES 4-1 4.1 Sampling Equipment and Procedures 4-1 4.2 Analytical Procedures 4-3 4.3 Quality Assurance Procedures 4-4 4.4 Calibration Procedures 4-4 4.4.1 Daily Quality Control Procedures 4-4 4.4.2 Duplicate Samples 4-4 4.4.3 Trip Blanks 4-6 4.4.4 Precision 4-6 4.4.5 Accuracy 4-6 5.0 RESULTS 5-1 5.1 Analytical Results 5-1 5.2 Analysis Result Statistics 5-1 5.3 Analytical Results Data 5-15 6.0 DATA ANALYSIS 6-1 6.1 Introduction 6-1 6.2 Summary Statistics 6-2 6.3 Box Plots 6-4 6.4 Seasonal ity 6-4 6.5 Intercarbonyl Correlations 6-25 6.6 Precision and Percent Differences 6-25 6.7 Audit Samples 6-33 7.0 CONCLUSIONS 7-1 8.0 REFERENCES 8-1 :S2O45/can.208f CarDonvl 1990 Final Reoon •; ; 1 ------- TABLE OF CONTENTS - Continued APPENDICES A Site Information from AIRS B Summary Statistics for Cases 1 and 2 for All Sites C Analytical Data Listing :52-045/can.208f Carbonyl 1990 Final Reoort 1 V ------- LIST OF FIGURES Page 3-1 1990 UATMP Carbonyl Data Flow 3-4 4-1 Urban Air Toxics Monitoring Program Canister Sampling System ... 4-2 4-2 Carbonyl Field Data Sheet 4-5 5-1 Average Carbonyl Concentrations - All Sites . 5-2 5-2 Carbonyl Concentration for Baton Rouge, Louisiana 5-3 5-3 Carbonyl Concentration for Chicago, Illinois 5-4 5-4 Carbonyl Concentration for Camden, New Jersey 5-5 5-5 Carbonyl Concentration for Houston, Texas 5-6 5-6 Carbonyl Concentration for Orlando, Florida 5-7 5-7 Carbonyl Concentration for Pensacola, Florida 5-8 5-8 Carbonyl Concentration for Port Neches, Texas 5-9 5-9 Carbonyl Concentration for Sauget, Illinois 5-10 5-10 Carbonyl Concentration for Toledo, Ohio 5-11 5-11 Carbonyl Concentration for Washington, D.C. - Site 1 5-12 5-12 Carbonyl Concentration for Wichita, Kansas 5-13 5-13 Carbonyl Concentration for Washington, D.C. - Site 2 5-14 6-1 Formaldehyde Box Plots for Case 1 6-11 6-2 Acetaldehyde Box Plots for Case 1 6-12 6-3 Acetone Box Plots for Case 1 6-13 6-4 Formaldehyde, Acetaldehyde, and Acetone Monthly Concentrations - All Sites 6-15 6-5 Formaldehyde Concentration Monthly Variation for 1990 for Selected Sites - Group 1 6-16 6-6 Formaldehyde Concentration Monthly Variation for 1990 for Selected Sites - Group 2 6-17 6-7 Formaldehyde Concentration Monthly Variation for 1990 for Selected Sites - Group 3 6-18 :S2-045/can.20af Caroonvi 1990 Final Heoort ------- LIST OF FIGURES - Continued Page 6-8 Acetaldehyde Concentration Monthly Variation for 1990 for Selected Sites - Group 1 5.19 5-9 Acetaldehyde Concentration Monthly Variation for 1990 for Selected Sites - Group 2 5.20 6-10 Acetaldehyde Concentration Monthly Variation for 1990 for Selected Sites - Group 3 6-21 6-11 Acetone Concentration Monthly Variation for 1990 for Selected Sites - Group 1 5.22 6-12 Acetone Concentration Monthly Variation for 1990 for Selected Sites - Group 2 6-23 6-13 Acetone Concentration Monthly Variation for 1990 for Selected Sites - Group 3 6-24 6-14 Formaldehyde/Acetaldehyde Correlation 6-27 6-15 Formaldehyde/Acetone Correlation 6-28 6-16 Acetaldehyde/Acetone Correlation 6-29 6-17 Quality Assurance - Audit Results, July 23, 1990 - Jan. 31, 1991 . 6-36 6-18 Quality Assurance - Audit Results, Mar. 31, 1991 - Apr. 24, 1991 . 6-37 :=2-045/can.208f Carbonyi 1990 Final Heoort y -j ------- LIST OF TABLES Page 2-1 1990 UATMP Target Compounds 2-2 3-1 1990 Urban Air Toxics Monitoring Program Sites 3-2 6-1 Probabilities for a Smaller W Statistic for Distributions of the Mean Concentrations and Logs of the Mean Concentrations ... 6-3 6-2 Summary Arithmetic and Lognormal Statistics for Mean Formaldehyde Concentrations: Case 1 5.5 6-3 Summary Arithmetic and Lognormal Statistics for Mean Formaldehyde Concentrations: Case 2 6-6 6-4 Summary Arithmetic and Lognormal Statistics for Mean Acetaldehyde Concentrations: Case 1 5.7 6-5 Summary Arithmetic and Lognormal Statistics for Mean Acetaldehyde Concentrations: Case 2 6-8 6-6 Summary Arithmetic and Lognormal Statistics for Mean Acetone Concentrations: Case 1 5.9 6-7 Summary Arithmetic and Lognormal Statistics for Mean Acetone Concentrations: Case 2 6-10 6-8 Correlations and Covariances between the Mean Concentrations of Formaldehyde, Acetaldehyde, and Acetone: Case 1 6-26 6-9 Summary of Formaldehyde Precision Statistics 6-30 6-10 Summary of Acetaldehyde Precision Statistics 6-31 6-11 Summary of Acetone Precision Statistics 6-32 6-12 Spiked Quality Assurance Cartridge Results for 1990 UATMP Monitoring 5.34 :S2-045/can.20ef Caroonvi 1990 Final Reoort ------- SYMBOLS AND ABBREVIATIONS ADL Analytical detection limit AIRS Atmospheric Information Retrieval System APR April AREAL Atmospheric Research and Exposure Assessment Laboratory AUG August BRLA Baton Rouge, LA; AIRS No. 22-033-0006 C4IL Chicago. IL; AIRS No. 17-031-0060 CANJ Camden, NJ; AIRS No. 34-007-0003 COR correlation coefficient COV covariance DC District of Columbia DEC December DIP Difference; Percent DIP = (X2 -X1)/((X1 + X2)/2)*100 DNPH 2,4-dinitrophenylhydrazine EPA I). S. Environmental Protection Agency P Friday FID Flame ionization detection FL .Florida FEB February GC/MS Gas chromatograph/mass spectrometry GC/MD Gas chromatograph/multidetector H1TX Houston, TX; AIRS No. 48-201-1034 Hg Mercury HPLC High pressure liquid chromatography ID Radian assigned alphanumeric identification IL Illinois in. inch JAN January JUL July JUN June KS Kansas L Liter LA Louisiana LOG natural logarithm :52-045/can.208f i 1990 Final Reoort V i ------- SYMBOLS AND ABBREVIATIONS (Continued) M MAR min. mL N NC NJ nm NMOC NOV OCT OH ORFL PEFL PID PNTX ppbv QA QAPP f\ /* QC QAD R RTP SAIL SAS® SEP Sn St STD T Th TLOH TX U. S. UATMP W W W1DC W1KS W2DC Monday March minute (60 seconds) milliliter number of cases, or sample size North Carolina New Jersey nanometer Nonmethane Organic Compound(s) November October Ohio Orlando, FL; AIRS No. 12-095-2002 Pensacola, FL; AIRS No. 12-033-0004 Photoionization detection Port Neches, TX; AIRS No. 48-245-4007 parts per billion by volume Qual ity Assurance Quality Assurance Project Plan Quality Control Quality Assurance Division regression coefficient Research Triangle Park, NC Sauget, IL; AIRS No. 17-163-1010 Statistical Analysis System September Sunday Saturday Standard Deviation Tuesday Thursday Toledo, OH; AIRS No. 39-095-0081 Texas United States of America Urban Air Toxics Monitoring Program Wednesday Shapiro-Wilk W statistic, used in SAS® software to indicate normality of a distribution Washington, DC; AIRS No. 11-001-0025 Wichita, KS; AIRS No. 20-173-0010 Washington, DC; AIRS No. 11-001-0039 252-045/can.208f Caroonyi 1990 Final Heoort ------- 1.0 SUMMARY AND CONCLUSIONS This report summarizes the results of sampling ambient air for selected carbonyl containing compounds in 12 urban centers in the contiguous United States as part of the Urban Air Toxics Monitoring Program (UATMP). Formaldehyde, acetaldehyde, and acetone concentrations were measured using 2,4-dinitrophenylhydrazine (DNPH)-coated silica cartridges to collect the carbonyls for subsequent analysis. Sampling and analysis followed guidance provided in U.S. Environmental Protection Agency (EPA) compendium method TO-11. Formaldehyde concentrations ranged from 0.42 to 34.5 ppbv with an average concentration for all sites of 4.2 ppbv. Site average formaldehyde concentrations ranged from 1.5 ppbv for Houston, TX (H1TX) to 7.9 for Washington, DC (W2DC). Acetaldehyde concentrations ranged from 0.37 to 9.5 ppbv, averaging 1.7 ppbv over all 1990 UATMP sites. Site average acetaldehyde concentrations ranged from 0.76 ppbv at Houston, TX (H1TX) to 2.5 ppbv at Baton Rouge, LA (BRLA). Acetone concentrations ranged from 0.37 to 10.8 ppbv and averaged 1.8 ppbv over all sites. Site average acetone concentrations ranged from 0.68 ppbv at Houston, TX (H1TX) to 2.9 ppbv at Chicago, IL (C4IL). The precision as measured by the mean percent difference over all sites was near 12% for formaldehyde, near 13% for acetaldehyde, and near 15% for acetone. At individual sites the mean percent differences ranged roughly from 4 to 30% for formaldehyde, from 7 to 30% for acetaldehyde, and from 8 to 23% for acetone. Accuracy was measured as bias from audit samples. For formaldehyde, bias ranged from -45.1 to 10.6% and averaged -4.6 percent. For acetaldehyde, bias ranged from -41.7 to 100.0% and averaged -1.2 percent. For acetone, bias ranged from -53.4 to 100.0% and averaged -4.3 percent. The average percent difference and biases reported in this study indicate that the sampling and analytical methodology is repeatable and valid. Concentration data for formaldehyde, acetaldehyde, and acetone appeared to be distributed approximately lognormal for sites in the 1990 UATMP. Average monthly concentrations differed from month to month over all sites and :a2-045/can.208f :a.-aonyi 1990 Final Reoort 1 - 1 ------- from site to site. Lowest average monthly concentrations appeared to be in May while concentrations appeared to peak in the fall months. Formaldehyde and acetaldehyde concentrations correlate well at all sites. Little correlation exists between acetone and either formaldehyde or acetaldehyde. :S2-045/can.208f CarOonvi 1990 Final Renort 1 - £ ------- 2.0 INTRODUCTION The U.S. EPA developed the UATMP Program to help state and local agencies assess the nature and magnitude of the toxic compounds in the air. The UATMP sampler collects ambient air samples at urban sites in 6-liter (L) SUMMA®-treated stainless steel canisters. At the same time, through a separate heated sample line, ambient air samples for carbonyl compound analysis are drawn in parallel through duplicate cartridges which trap the carbonyl compounds from the ambient air. The UATMP is a companion program to the Nonmethane Organic Compound (NMOC) Monitoring Program which began in the summer of 1984. The NMOC Monitoring Program measures the total concentration of organic compounds, with the exception of methane, but does not speciate organics. The UATMP speciates 38 toxic compounds listed in Table 2-1, primarily aromatic hydrocarbons and halocarbons. UATMP ambient air samples are collected in 6-L stainless steel canisters. The carbonyl cartridges collected at the UATMP sites for 1990 were extracted and analyzed by the Atmospheric Research and Exposure Assessment Laboratory (AREAL) of the U.S. EPA at Research Triangle Park, North Carolina, for formaldehyde, acetaldehyde, and acetone. This report presents the data summaries and other data assessments for the carbonyl samples collected during the 1990 UATMP season. The 1990 UATMP season began in March 1990 and ended in February 1991. The air toxics compounds collected in canisters for the 1990 UATMP season are reported separately.1-2 C52-045/can.208f i 1990 Final fleoort ? - 1 ------- Table 2-1 1990 UATMP Target Compounds Canister Analvtes Cartridge Analvtes Acetylene Propylene 1,3-Butadiene Vinyl chloride Chloromethane Chloroethane Bromomethane Methylene chloride trans- 1,2-Dichloroethylene 1,1-Dichloroethane Chloroprene Bromochloromechane Chloroform 1,1,1-Trichloroethane Carbon tetrachloride 1,2-Dichloroethane Benzene Trichloroethylene 1,2-Dichloropropane Bromodichloromethane trans-1,3-Dichloropropylene Toluene n-Octane cis-l,3-Dichloropropyiene 1,1,2-Trichloroethane Tetrachloroethylene Dibromochloromethane Chlorobenzene Ethylbenzene ra/p-Xylene Styrene o-Xylene Bromoform 1,1,2,2-Tetrachloroethane m-Dichlorobenzene p-Dichlorobenzene o-Dichlorobenzene Formaldehyde Acetaldehyde Acetone :32-045/can.208( Cjroonvi 1990 Final Reoort 2-2 ------- 3.0 UATMP FOR 1990 Brief program descriptions for the air toxics and carbonyl portions of the UATMP are given in this section. Both the air toxics and carbonyl programs collected 24-hour integrated ambient air samples on a once every 12-day schedule beginning the week of March 12, 1990. Sampling for the 1990 UATMP was completed on February 23, 1991. Whole-air ambient air samples were collected in 6-L SUMMA®-treated stainless steel canisters and on DNPH-treated cartridges at 12 sites shown in Table 3-1. The table also gives Radian site codes, Aerometric Information Retrieval System (AIRS) Numbers, and EPA Regions. Additional description of the sites from the AIRS data base are given in Appendix A. Carbonyl samples were taken simultaneously with all the UATMP canister samples. Duplicate cartridges were installed in parallel in a separate heated sample probe. Ambient air was drawn through the carbonyl cartridges for 24 hours at a constant flow rate. The flow rate, which is in the range of 600 to 1200 mL/min., is measured at each site by the site operator before and after taking each sample. Carbonyl cartridges are filled with DNPH-coated silica which reacts with carbonyls in ambient air, trapping them in the cartridge. Ozone was removed from ambient air collected in the 1990 program through the use of an ozone denuder. This ozone denuder was added to the sampling system after the heated probe to eliminate ozone, which is an interferant with the DNPH. The use of an ozone denuder in the sampling system resulted in higher reported formaldehyde concentrations. The removal efficiency of each ozone denuder was verified prior to, and at the completion of, the field sampling. The removal efficiency of all ozone denuders was measured at > 99.9% using 120 ppb ozone test mixture. In conjunction with the 1990 UATMP program, a comparison of ozone scrubbed and unscrubbed DNPH cartridges was conducted and are reported elsewhere.3 Three laboratories are involved in the carbonyl cartridge preparation, distribution and analysis. An independent EPA contractor prepares carbonyl ;=2-045/can.208f CarOonvi 1990 Final Heoort 3-1 ------- II III IV V VI VII Table 3-1 1990 Urban Air Toxics Monitoring Program Sites City Camden, NJ Washington, DC Washington, DC Orlando, FL Pensacola, FL Chicago, IL Sauget, IL Toledo, OH Houston, TX Baton Rouge, LA Port Neches, TX Wichita, KS Radian Site Code CANJ W1DC W2DC ORFL PEFL C4IL SAIL TLOH H1TX BRLA PNTX W1KS AIRS Number 34-007-0003 11-001-0025 11-001-0039 12-095-2002 12-033-0004 17-031-0060 17-163-1010 39-095-0081 48-201-1034 22-033-0006 48-245-4007 20-173-0010 :52-045/can.208f ^roonyl 1990 Final Reoon 3-2 ------- sampling cartridges in batches. The Radian RTF laboratory obtained the prepared cartridges for distribution in the shipping boxes containing the canisters that are sent to the UATMP sites, along with the carbonyl field data sheet. Radian coordinates the distribution of the carbonyl sample cartridges, and custody records to the U.S. EPA AREAL for analysis. EPA's AREAL extracts samples from the cartridges and analyzes these extracts for target compounds. Radian Corporation reviews the analytical results, summarizes the data, and is responsible for semi-annual and annual result summaries, which are distributed to EPA and participating agencies. Figure 3-1 shows the carbonyl sample and data flow for the 1990 UATMP. :52-045/cah.208f Caroonyi 1990 F,na! fleoort 3 _ 7 ------- EPA Contractor Praoo* AJdahyaa CarUidQB* Lot of 300 Radan Oaftfeudon ofCarMgMwth Radan-PPK Calcutta flow Rate Tranefar to Coaacoan LOTUSr ! °^Fflini Tf w«h LOTUS taS>A(A8EAL) AAEALVtnfy Straw Action Radan of Radan p ^TLT0^ 1 S£ OAQPS. For Ocfcata PraeaMon Radan FtnatRaport NOI R«far UhasnanM |cKJ OataPoktttoAREAL 1 Olatrtuta ToRadonai Stata, and Local Contacts Figure 3-1. 1990 UATMP Carbonyl Data Flow -3»5.C3n iCSf scnvi 1990 F-nai fleoon 3 " 4 ------- 4.0 SAMPLING, ANALYSIS, AND QUALITY ASSURANCE PROCEDURES Sampling and analysis procedures for the carbonyl samples, along with the quality assurance procedures used to quantify data quality are described in this section. Implementing the UATMP involved Radian personnel installing the sampling equipment for the canister and the carbonyl samples, training site personnel to operate the equipment properly, observing all the quality assurance procedures necessary to ensure the integrity of the sample, and providing appropriate documentation. The site operators' task involved recognizing problems with sampling equipment and procedures, and notifying Radian personnel at Research Triangle Park so that appropriate corrective action might be taken. 4.1 SAMPLING EQUIPMENT AND PROCEDURES A schematic diagram of the UATMP sampler is shown in Figure 4-1. The sampler consists of two subsystems, the VOC canister and the carbonyl cartridge. Each subsystem collects a discrete sample through use of a common control system. Each sampler subsystem has separate atmospheric inlet. The ambient air is introduced through an inverted glass funnel and heated stainless steel probe. The heated probe was maintained at 150°F to prevent moisture condensation. The carbonyl cartridges are mounted in parallel, so that the carbonyl samples are collected in duplicate during each sampling episode. The carbonyl cartridge is a commerically available (Waters Co.) silica gel Sep-pak® cartridge which is coated with DNPH. The cartridges are prepared in batches by the laboratory and stored under refrigeration until shipped to the field. The carbonyl cartridges are installed in the sample line several days ahead of the scheduled sample collection. The collection frequency was planned once every 12 days (30 per year). A 24-hour sample collection period was utilizied for both the canister and cartridge samples. The carbonyl probe was purged and heated prior to sample collection period. Each carbonyl cartridge has a unique serial number which is recorded on the custody records. In :52O45/can.208f Z-irQonyi 1990 Final fleoort 4-1 ------- o 5 > LU •^ j^ (/) .1 £ 0 O a> ~ c o § * 0 C a c3 c — — CD E ° |